GENERAL - WASTE MANAGEMENT

CONTENTS Sections Definitions 1 Designation and Exemption of Wastes 2-3 Waste Disposal Sites and Waste Management Systems 4-10 Standards for Waste Disposal Sites 11-16.1 Management of Asbestos Waste 17 Waste Generation Facilities 17.1-17.2 Generator Registration 18 Manifests — Generator Requirements 19 Manifests — Carrier Requirements 20-22 Manifests — Transport within Ontario 23 Manifests — Transport out of Ontario 24 Manifests — Transport into Ontario 25 Manifests — Transport through Ontario 26 Fees 26.1 Refusals 27 Submission of Information to Registry 27.1-27.2 On-Site Thermal Treatment Equipment 28 Woodwaste Combustor Sites 28.1-28.2 Waste-Derived Fuel Sites 28.3-28.6 Existing Hospital Incinerators 29 Field Operations 29.1-29.5 Waste from Covid-19 Antigen Point-of-Care Testing 29.6 Stationary Refrigerant Waste 30-35 Mobile Refrigerant Waste 36-42 Selected Waste Depots 42.1-42.17-60 Pesticide Container Depots 61-73 Land Disposal of Hazardous Waste 74-85 Schedule 1 Hazardous industrial waste Schedule 1.1 Exempt hazardous industrial wastes Schedule 2 Part a — acute hazardous waste chemical Schedule 2 Part b — hazardous waste chemical Schedule 2.1 Exempt acute hazardous waste chemicals Schedule 2.2 Exempt hazardous waste chemicals Schedule 3 Severely toxic contaminants Schedule 4 Leachate quality criteria Schedule 5 Land disposal treatment requirements for characteristic wastes Schedule 6 Universal treatment standards (uts) for characteristic wastes Schedule 7 Treatment methods and standards Schedule 8 Alternative treatment for hazardous debris Schedule 9 Test method for the determination of “liquid waste” (slump test)* Definitions 1. (1) In this Regulation, “access road” means a road that leads from a public road to a waste disposal site; “acute hazardous waste chemical” means, (a) a commercial waste chemical listed as an acute hazardous waste chemical in Part A of Schedule 2, other than a waste described in Schedule 2.1, (b) a mixture of a waste referred to in clause (a) and any other waste or material, or (c) a waste derived from a waste referred to in clause (a), unless, (i) the waste that is derived from the waste referred to in clause (a) is listed in Schedule 2.1, or (ii) the waste that is derived from the waste referred to in clause (a) is produced in accordance with an environmental compliance approval that states that, in the opinion of the Director, the waste that is produced in accordance with the approval does not have characteristics similar to the characteristics of the acute hazardous waste chemical from which it was derived; “agricultural waste” means waste generated by a farm operation activity, but does not include, (a) domestic waste that is human body waste, toilet or other bathroom waste, waste from other showers or tubs, liquid or water borne culinary waste, (b) waste from a sewage works within the meaning of the Ontario Water Resources Act, if one of the criteria set out in subsection (1.0.1) is met; (c) a dead farm animal within the meaning of Ontario Regulation 106/09 (Disposal of Dead Farm Animals) made under the Nutrient Management Act, 2002 or a regulated dead animal within the meaning of Ontario Regulation 105/09 (Disposal of Deadstock) made under the Food Safety and Quality Act, 2001, (d) inedible material within the meaning of Ontario Regulation 31/05 (Meat) made under the Food Safety and Quality Act, 2001, or (e) any material that is condemned or derived from a carcass at a registered establishment within the meaning of the Meat Inspection Act (Canada); “anaerobic digestion” means the decomposition of organic matter by bacteria in an oxygen-limiting environment; “anaerobic digestion materials” means materials that are intended for treatment in a mixed anaerobic digestion facility, whether the materials are generated at the agricultural operation or received at the agricultural operation from an outside source; “anaerobic digestion output” means any solid or liquid material that results from the treatment of anaerobic digestion materials in a mixed anaerobic digestion facility; “aqueous waste” means waste that is aqueous and contains less than 1 per cent total organic carbon by weight and less than 1 per cent total suspended solids by weight; “asbestos waste” means the following solid or liquid waste that contains asbestos in more than a trivial amount: 1. Waste that results from the removal of asbestos-containing construction or insulation materials. 2. Waste that results from the manufacture of asbestos-containing products. 3. Waste that results from the removal of asbestos-containing components from a motor vehicle. 4. Waste that results from the removal or handling of waste or materials described in paragraphs 1, 2 and 3, including personal protective equipment, tools that cannot be decontaminated and cleaning materials; “biodiesel” means a fuel or fuel component that is comprised of mono-alkyl esters of long-chain fatty acids that are derived from plant oils or animal fats, if the fuel or fuel component, (a) conforms to the detailed requirements shown in Table 1 of ASTM International Standard D6751, entitled “Standard Specification for Biodiesel Fuel Blend Stock (B100) for Middle Distillate Fuels”, as amended from time to time, when tested by the test methods indicated in that Standard, or (b) is in accordance with the limits specified in Table 1 of European Standard EN 14214, entitled “Automotive Fuels – Fatty acid methyl esters (FAME) for diesel engines – Requirements and test methods”, as amended from time to time, when tested by the test methods indicated in that Standard; “carrier” means the operator of a waste transportation system; “cell”, in respect of a landfilling site, means a deposit of waste that has been sealed by cover material so that no waste deposited in the cell is exposed to the atmosphere; “characteristic waste” means hazardous waste that is, (a) corrosive waste, (b) ignitable waste, (c) leachate toxic waste, or (d) reactive waste; “commercial waste” includes asbestos waste; “commercial waste chemical” means a waste that is or contains a commercial chemical product or manufacturing chemical intermediate of a specified generic name and includes, (a) an off-specification commercial chemical product or manufacturing chemical intermediate which, if it met specifications, would have the specified generic name, (b) residues or contaminated material from the clean-up of a spill of a commercial chemical product or manufacturing chemical intermediate of the specified generic name or of an off-specification commercial chemical product or manufacturing chemical intermediate which, if it met specifications, would have the specified generic name, or (c) an empty container or the liner from an empty container that contained a commercial chemical product or manufacturing chemical intermediate of the specified generic name, or an off-specification commercial chemical product or manufacturing chemical intermediate which, if it met specifications, would have the specified generic name, or residues or contaminated materials from the clean-up of a spill of any of them, unless the empty container or the liner from the empty container has been triple rinsed, but, except as specified in clause (a), (b) or (c), does not include a waste stream or waste material contaminated with material of the specified generic name; “common mercury waste” means, (a) electrical switches, thermostats or fluorescent lamps that contain mercury and that are damaged, worn out or discarded, (b) thermometers, barometers or other measuring devices that contain mercury and that are damaged, worn out or discarded, (c) discarded material that contains mercury from dental procedures carried out by a member of the Royal College of Dental Surgeons of Ontario; “common mercury waste recovery facility” means a site at which common mercury waste is received for recovery of mercury and at which no disposal of common mercury waste or of mercury takes place; “composting” means the treatment of waste by aerobic decomposition of organic matter by bacterial action for the production of stabilized humus; “composting facility” means a facility, (a) where composting is carried out, and (b) in respect of which an environmental compliance approval has been issued under Part II.1 of the Act; “composting material” has the same meaning as in Ontario Regulation 105/09 (Disposal of Deadstock) made under the Food Safety and Quality Act, 2001; “corrosive waste” means, (a) a waste that is aqueous and has a pH less than or equal to two or greater than or equal to 12.5 as determined by a pH meter, (b) a waste that is a liquid and corrodes steel (SAE 1020) at a rate greater than 6.35 millimetres per year at a test temperature of 55° Celsius using test NACE TM-01-69 or an equivalent test approved by the Director, or (c) a waste that is a solid and, when prepared in a mixture or solution with distilled water that is 50 per cent waste by weight, has a pH less than or equal to two or greater than or equal to 12.5 as determined by a pH meter, other than, (i) solid incinerator ash or fly-ash from a woodwaste combustor site, or (ii) solid wastes generated by a manufacturer of pulp, paper, recycled paper, corrugated cardboard or other paper products; “cover material” means soil or other material approved for use in sealing cells in landfilling; “cured compost” has the same meaning as in Ontario Regulation 105/09 (Disposal of Deadstock) made under the Food Safety and Quality Act, 2001; “disposal facility” has the same meaning as in Ontario Regulation 105/09 (Disposal of Deadstock) made under the Food Safety and Quality Act, 2001; “domestic waste” includes asbestos waste; “dump” means a waste disposal site where waste is deposited without cover material being applied at regular intervals; “dust suppressant” means a waste used for dust suppression in accordance with an environmental compliance approval in respect of a dust suppression waste management system; “dust suppression site” means a waste disposal site where dust suppressant is deposited; “electroplating” includes common and precious metal electroplating, anodizing, chemical etching and milling, and includes cleaning and stripping associated with common and precious metal electroplating, anodizing, chemical etching and milling, but does not include chromating, phosphating, immersion plating, colouring or other chemical conversion coating, electroless plating or printed circuit board manufacturing; “empty container” means a container from which all wastes and other materials have been removed using the removal practices such as pumping or pouring commonly used for the specific materials and that contains less than 2.5 centimetres of material on the bottom of the container; “end-of-life vehicle” has the same meaning as in Ontario Regulation 85/16 (Registrations under Part II.2 of the Act - End-of-life Vehicles) made under the Act; “end-of-life vehicle waste disposal site” has the same meaning as in Ontario Regulation 85/16; “engineered facility” means, in respect of a landfilling site, anything affixed to or made part of land that is intended to be a functional element or feature of the landfilling site for more than five years and that is created or put in place by human activity; “excess soil” has the same meaning as in Ontario Regulation 406/19 (On-Site and Excess Soil Management) made under the Act; “existing hospital incinerator” means an incinerator put into operation before the 31st day of December, 1985 owned by a hospital within the meaning of the Public Hospitals Act at which pathological waste but no hauled liquid industrial waste or other hazardous waste is incinerated; “farm operation” means an agricultural, aquacultural or horticultural operation, other than a race track or a zoo, that is engaged in any or all of the following: 1. Growing, producing or raising farm animals. 2. The production of agricultural crops, including greenhouse crops, maple syrup, mushrooms, nursery stock, tobacco, trees and turf grass. 3. The processing, by the operator of the farm operation, of anything mentioned in paragraphs 1 and 2, where the processing is primarily in relation to products produced from the agricultural, aquacultural or horticultural operation. 4. The use of transport vehicles by the operator of the farm operation, to transport anything mentioned in paragraphs 1 and 2, where the use of transport vehicles is primarily in relation to products produced from the agricultural, aquacultural or horticultural operation; “farm operation activity” means an activity mentioned in paragraphs 1 to 4 of the definition of “farm operation”; “field operations” means operations that, (a) take place at a location that is not, (i) the primary place of business of the person who undertakes the operations, (ii) a warehouse, factory or production plant of the person who undertakes the operations, or (iii) a local waste transfer facility, (b) involve mobile health care, take place at a location that is owned or controlled by the person who undertakes the operations or take place in accordance with the written agreement of the person who owns or controls the location where the operations take place, (c) are not primarily waste management operations, and (d) primarily involve, (i) construction, demolition or renovation, (ii) mining, (iii) servicing, maintaining or monitoring, (iv) the operation of a utility, including communication networks, electric power lines or pipelines, (v) the operation of highways, including a facility dedicated to the maintenance and upkeep of a section of highway, (vi) environmental, geophysical or agricultural field testing, (vii) mobile health care, (viii) the supply of medical equipment or medication directly to the home of a human being to whom mobile health care is provided, (ix) the operation of a specimen collection centre, (x) the transportation in a vehicle of specimens and waste generated by the collection of specimens from a specimen collection centre, if, (A) the specimens and waste result from the operation of the specimen collection centre, (B) the sole purpose for which the vehicle is being operated is to transport the specimens and waste, and (C) the specimens and waste are transported to a laboratory associated with the operation of the specimen collection centre, (xi) spill clean-up or emergency response activities, if the person engaging in those activities is, (A) the owner of the spilled material, (B) a person who had control of the spilled material, (C) a municipality, (D) a person or member of a class of persons designated for the purposes of clause 100 (1) (c) of the Act, (E) a person who has jurisdiction and control over a highway, (F) a person who holds an environmental compliance approval issued in respect of an activity mentioned in subsection 27 (1) of the Act authorizing spill clean-up or emergency response activities, (G) the Ministry, (H) a police service, or (I) a fire department, (xii) housekeeping, maintenance and collection and removal of litter, rubbish, abandoned or discarded material and debris on or near a highway by a person who has jurisdiction and control over the highway, (xiii) housekeeping, maintenance and collection and removal of littered, abandoned or discarded needles and syringes on or near parks, beaches or other public property by a person responsible for the maintenance of the property, or (xiv) activities associated with operating trade shows, exhibitions or other temporary events; “fly-ash” means particulate matter removed from combustion flue gases; “food processing and preparation operations” include food packing, food preserving, wine making, cheese making and restaurants; “generator” means the operator of a waste generation facility; “generator registration document” has the same meaning as set out in Ontario Regulation 323/22 (Subject Waste Program) made under the Resource Recovery and Circular Economy Act, 2016; “Generator Registration Report” means the report required under section 18; “GNF” means GNF within the meaning of Ontario Regulation 300/14 made under the Nutrient Management Act, 2002 that is generated at a greenhouse operation that is registered under that regulation; “grinding” means the treatment of waste by uniformly reducing the waste to particles of controlled maximum size; “hauled liquid and hazardous waste collection system” means a waste management system or any part thereof for the collection, handling, transportation, storage or processing of hauled liquid industrial waste or hazardous waste but does not include the disposal thereof; “hauled liquid industrial waste” means liquid industrial waste transported in a tank or other container for treatment or disposal; “hauled sewage” means, (a) domestic waste that is human body waste, toilet or other bathroom waste, waste from other showers or tubs, liquid or water borne culinary or sink waste or laundry waste, and (b) other waste that is suitable for storage, treatment or disposal in a sewage system regulated under Part 8 of Division B of Ontario Regulation 332/12 (Building Code) made under the Building Code Act, 1992, if the waste is not fully disposed of at the site where it is produced, other than, (i) waste that is, (A) from a sewage works that is subject to an environmental compliance approval, and (B) conveyed, by a sewer that is subject to an environmental compliance approval, away from the site where it is produced, (ii) waste in a vehicle sewage holding tank, or (iii) GNF; “hazardous industrial waste” means, (a) a waste listed as a hazardous industrial waste in Schedule 1, other than a waste described in Schedule 1.1, (b) a mixture of a waste referred to in clause (a) and any other waste or material, or (c) a waste derived from a waste referred to in clause (a), unless, (i) the waste that is derived from the waste referred to in clause (a) is listed in Schedule 1.1, or (ii) the waste that is derived from the waste referred to in clause (a) is produced in accordance with an environmental compliance approval that states that, in the opinion of the Director, the waste that is produced in accordance with the approval does not have characteristics similar to the characteristics of the hazardous industrial waste from which it was derived; “hazardous waste” means a waste that is a, (a) hazardous industrial waste, (b) acute hazardous waste chemical, (c) hazardous waste chemical, (d) severely toxic waste, (e) ignitable waste, (f) corrosive waste, (g) reactive waste, (h) radioactive waste, except radioisotope wastes disposed of in a landfilling site in accordance with the written instructions of the Canadian Nuclear Safety Commission, (i) pathological waste, (j) leachate toxic waste, or (k) PCB waste, but does not include, (l) hauled sewage, (m) waste from the operation of a sewage works subject to the Ontario Water Resources Act where the works, (i) is owned by a municipality, (ii) is owned by the Crown or the Ontario Clean Water Agency, subject to an agreement with a municipality under the Ontario Water Resources Act, or (iii) receives only waste similar in character to the domestic sewage from a household, (n) domestic waste, (o) incinerator ash resulting from the incineration of waste that is neither hazardous waste nor liquid industrial waste, (p) waste that is a hazardous industrial waste, hazardous waste chemical, ignitable waste, corrosive waste, leachate toxic waste or reactive waste and that is produced in any month in an amount less than five kilograms or otherwise accumulated in an amount less than five kilograms, (q) waste that is an acute hazardous waste chemical and that is produced in any month in an amount less than one kilogram or otherwise accumulated in an amount less than one kilogram, (r) an empty container or the liner from an empty container that contained hazardous industrial waste, hazardous waste chemical, ignitable waste, corrosive waste, leachate toxic waste or reactive waste, (s) an empty container of less than twenty litres capacity or one or more liners weighing, in total, less than ten kilograms from empty containers, that contained acute hazardous waste chemical, (t) the residues or contaminated materials from the clean-up of a spill of less than five kilograms of waste that is a hazardous industrial waste, hazardous waste chemical, ignitable waste, corrosive waste, leachate toxic waste or reactive waste, or (u) the residues or contaminated materials from the clean-up of a spill of less than one kilogram of waste that is an acute hazardous waste chemical; “hazardous waste chemical” means, (a) a commercial waste chemical listed as a hazardous waste chemical in Part B of Schedule 2, other than a waste described in Schedule 2.2, (b) a mixture of a waste referred to in clause (a) and any other waste or material, or (c) a waste derived from a waste referred to in clause (a), unless, (i) the waste that is derived from the waste referred to in clause (a) is listed in Schedule 2.2, or (ii) the waste that is derived from the waste referred to in clause (a) is produced in accordance with an environmental compliance approval that states that, in the opinion of the Director, the waste that is produced in accordance with the approval does not have characteristics similar to the characteristics of the hazardous waste chemical from which it was derived; “highway” has the same meaning as in the Highway Traffic Act; “hospital incinerator” means an incinerator owned by a hospital within the meaning of the Public Hospitals Act; “ignitable waste” means a waste that, (a) is a liquid, other than an aqueous solution containing less than 24 per cent alcohol by volume and has a flash point less than 61° Celsius, as determined by the Tag Closed Cup Tester (ASTM D-56-79), the Setaflash Closed Cup Tester (ASTM D-3243-77 or ASTM D-3278-78), the Pensky-Martens Closed Cup Tester (ASTM D-93-79), or as determined by an equivalent test method approved by the Director, (b) is a solid and is capable, under standard temperature and pressure, of causing fire through friction, absorption of moisture or spontaneous chemical changes and, when ignited, burns so vigorously and persistently that it creates a danger, (c) is a Class 2.1 Flammable Gas within the meaning of paragraph 2.14 (a) of the Transportation of Dangerous Goods Regulations made under the Transportation of Dangerous Goods Act, 1992 (Canada), (d) is a Class 5.1 Oxidizing Substance within the meaning of paragraph 2.24 (a) of the Transportation of Dangerous Goods Regulations made under the Transportation of Dangerous Goods Act, 1992 (Canada), or (e) is a Class 5.2 Organic Peroxide within the meaning of paragraph 2.24 (b) of the Transportation of Dangerous Goods Regulations made under the Transportation of Dangerous Goods Act, 1992 (Canada); “incinerator ash” means the ash residue, other than fly-ash, resulting from incineration where the waste is reduced to ashes containing by weight less than 10 per cent of combustible materials; “incinerator waste” means the residue from incineration, other than incinerator ash and fly-ash; “individual collection system” means the collection of a householder’s own domestic wastes by a householder and the transportation of such wastes to a waste disposal site by the householder; “industrial waste” means waste, other than municipal waste, from, (a) an enterprise or activity involving warehousing, storage or industrial, manufacturing or commercial processes or operations, (b) research or an experimental enterprise or activity, (c) an enterprise or activity to which clause (a) would apply if the enterprise or activity were carried on for profit, (d) clinics that provide medical diagnosis or treatment, (e) schools, laboratories or hospitals, or (f) a facility or vehicle owned or operated by a municipality; “inert fill” means earth or rock fill or waste of a similar nature that contains no putrescible materials or soluble or decomposable chemical substances but does not include excess soil; “intact waste battery” means an electric battery that is intact but is damaged, spent, worn out or discarded; “in-vehicle sewage” means waste produced in a vehicle that is human body waste, toilet or other bathroom waste, waste from other showers or tubs, liquid or water borne culinary or sink waste, laundry waste or similar waste that would normally be carried away by a sewer if it were not produced in a vehicle; “laboratory” has the same meaning as in the Laboratory and Specimen Collection Centre Licensing Act; “land disposal” means, with respect to a waste, the deposit or disposal of the waste upon, into, in or through land, including, (a) the deposit of the waste at a dump, (b) the landfilling of the waste, (c) the discharge of the waste into a geological formation by means of a well, and (d) the landfarming of the waste, in the case of a petroleum refining waste, and “land disposed” has a corresponding meaning; “landfarming” means the biodegradation of petroleum refining wastes by naturally occurring soil bacteria by means of controlled application of the wastes to land followed by periodic tilling; “landfilling” means the disposal of waste by deposit, under controlled conditions, on land or on land covered by water, and includes compaction of the waste into a cell and covering the waste with cover materials at regular intervals; “leachate toxic waste” means a waste producing leachate containing any of the contaminants listed in Schedule 4 at a concentration equal to or in excess of the concentration specified for that contaminant in Schedule 4 using the Toxicity Characteristic Leaching Procedure; “liquid industrial waste” means waste that is both liquid waste and industrial waste but does not include, (a) hazardous waste, (a.1) hauled sewage, (a.2) GNF, (b) waste from the operation of a sewage works described in clause (m) of the definition of “hazardous waste”, (c) waste from the operation of a water works subject to the Ontario Water Resources Act or the Safe Drinking Water Act, 2002, (d) waste that is produced in any month in an amount less than twenty-five litres or otherwise accumulated in an amount less than twenty-five litres, (e) waste directly discharged by a generator from a waste generation facility into, (i) a sewage works, other than a storm sewer, that is subject to the Ontario Water Resources Act or was established before April 3, 1957, or (ii) a sewage system regulated under Part 8 of Division B of Ontario Regulation 332/12 (Building Code) made under the Building Code Act, 1992, (f) waste that results directly from food processing and preparation operations, (g) drilling fluids and produced waters associated with the exploration, development or production of crude oil or natural gas, (h) processed organic waste, or (i) asbestos waste; “liquid soil” has the same meaning as in Ontario Regulation 406/19 (On-Site and Excess Soil Management) made under the Act; “liquid waste” means waste that has a slump of more than 150 millimetres using the Test Method for the Determination of Liquid Waste (slump test) set out in Schedule 9; “listed waste” means hazardous waste that is, (a) an acute hazardous waste chemical, (b) hazardous industrial waste, (c) a hazardous waste chemical, or (d) severely toxic waste; “local waste transfer facility” means a site, (a) at which waste from field operations is received, bulked, temporarily stored and transferred, (b) that is owned or controlled by the person who undertakes the field operations referred to in clause (a) or by a person on whose behalf those field operations are undertaken, (c) at which no waste is received other than waste from field operations, and (d) that is used primarily for functions other than waste management; “lubricating oil” means petroleum-derived or synthetic crankcase oil, engine oil, hydraulic fluid, transmission fluid, gear oil, heat transfer fluid, or other oil or fluid used for lubricating machinery or equipment; “Manual” means the publication entitled “Registration Guidance Manual for Generators of Liquid Industrial and Hazardous Waste”, published by the Ministry of Environment and Energy and dated April 1995, as amended from time to time; “marine craft waste disposal system” means a waste disposal system operated by a person or a municipality for the receiving of waste from marine craft for deposit in holding tanks; “mixed anaerobic digestion” means anaerobic digestion of both on-farm anaerobic digestion materials and off-farm anaerobic digestion materials in the same facility; “mixed anaerobic digestion facility” means an anaerobic digestion facility that treats both on-farm anaerobic digestion materials and off-farm anaerobic digestion materials on a farm unit on which an agricultural operation is carried out; “mobile health care” means, (a) human or animal health care that takes place at, (i) the home of the human being or animal, (ii) a location at which emergency services or ambulance services are provided to the human being or animal, (iii) a location that is being used temporarily for health care providers to administer vaccinations to the human being or animal, or (iv) a location that is being used temporarily for the purpose of collecting blood or other specimens from the human being or animal, but does not include any care at that location that is related to the collection of specimens as part of conducting COVID-19 antigen POCT testing within the meaning of subsection 29.6 (1), (b) animal health care that, (i) is provided by a person licensed to engage in the practice of veterinary medicine by the Registrar of the College of Veterinarians of Ontario, and (ii) takes place at a temporary facility for which a certificate of accreditation has been issued by the Registrar of the College of Veterinarians of Ontario, but does not include health care that is provided at, (c) a hospital as defined in the Public Hospitals Act or a private hospital as defined in the Private Hospitals Act, (d) a psychiatric facility as defined in the Mental Health Act, (e) a long-term care home as defined in the Fixing Long-Term Care Act, 2021, (f) a home for special care as defined in the Homes for Special Care Act, (g) homes that are part of the Ontario Government program known as the “Community Homes for Opportunity” program, (h) the professional office of a member of the Royal College of Dental Surgeons of Ontario, (i) the professional office of a member of the College of Physicians and Surgeons of Ontario, (j) the professional office of a member of the College of Nurses of Ontario, (k) the professional office of a member of the College of Veterinarians of Ontario, or (l) a pharmacy in respect of which a certificate of accreditation has been issued under section 139 of the Drug and Pharmacies Regulation Act; “mobile refrigerant waste” means refrigerant removed from the air-conditioning, heat pump, refrigeration or freezer unit of anything used for the purposes of transportation; “mobile refrigerant waste collector” means a mobile refrigerant waste management system that collects mobile refrigerant waste it has removed from equipment in which refrigerant is used; “mobile refrigerant waste recycler” means a mobile refrigerant waste management system that receives mobile refrigerant waste from other mobile refrigerant waste management systems and recycles it; “municipal waste” means, (a) any waste, whether or not it is owned, controlled or managed by a municipality, except, (i) hazardous waste, (ii) liquid industrial waste, or (iii) gaseous waste, and (b) solid fuel, whether or not it is waste, that is derived in whole or in part from the waste included in clause (a); “non-aqueous waste” means waste that is not aqueous waste; “non-hazardous solid industrial waste” means industrial waste that is not liquid industrial waste and is not hazardous waste and includes asbestos waste; “off-farm anaerobic digestion materials” means anaerobic digestion materials that are not generated at an agricultural operation and that are received at an agricultural operation from an outside source; “on-farm anaerobic digestion materials” means anaerobic digestion materials that are generated at an agricultural operation; “on-site garbage grinder” means a grinder, (a) used for the treatment of waste that is subsequently discharged as sewage, and (b) located in a building or structure used principally for functions other than waste management; “on-site incinerator” means an incinerator located at a site used principally for functions other than waste management in which only waste generated on that site is incinerated; “on-site road” means a road for the movement of vehicles and equipment within a waste disposal site; “on-site thermal treatment equipment” means thermal treatment equipment located at a site used principally for functions other than waste management in which only waste generated on that site is subject to thermal treatment, and includes an on-site incinerator; “organic soil conditioning” means the incorporation of processed organic waste in the soil to improve its characteristics for crop or ground cover growth; “packing and baling” means the treatment of waste by its compression into blocks or bales and binding or sheathing the blocks with wire, metal, plastic or other material; “pathological waste” means, (a) any part of the human body, including tissues and bodily fluids, but excluding fluids, extracted teeth, hair, nail clippings and the like, that are not infectious, (b) any part of the carcass of an animal infected with a communicable disease or suspected by a licensed veterinary practitioner to be infected with a communicable disease, (c) non-anatomical waste infected with communicable disease, (d) a mixture of a waste referred to in clause (a), (b) or (c) and any other waste or material, or (e) a waste derived from a waste referred to in clause (a), (b) or (c), unless the waste that is derived from the waste referred to in clause (a), (b) or (c) is produced in accordance with an environmental compliance approval that states that, in the opinion of the Director, the waste that is produced in accordance with the approval does not have characteristics similar to the characteristics of pathological waste referred to in clause (a), (b) or (c); “PCB” has the same meaning as in Regulation 362 of the Revised Regulations of Ontario, 1990 (Waste Management — PCBs) made under the Act; “PCB waste” has the same meaning as in Regulation 362 of the Revised Regulations of Ontario, 1990 (Waste Management — PCBs) made under the Act; “processed organic waste” means waste that is predominantly organic in composition and has been treated by aerobic or anaerobic digestion, or other means of stabilization, and includes sewage residue from sewage works that are subject to the provisions of the Ontario Water Resources Act; “radioactive waste” includes, (a) a mixture of radioactive waste and any other waste or material, and (b) a waste derived from radioactive waste, unless the waste that is derived from the radioactive waste is produced in accordance with an environmental compliance approval that states that, in the opinion of the Director, the waste that is produced in accordance with the approval does not have characteristics similar to the characteristics of radioactive waste; “reactive waste” means a waste that, (a) is normally unstable and readily undergoes violent change without detonating, (b) reacts violently with water, (c) forms potentially explosive mixtures with water, (d) when mixed with water, generates toxic gases, vapours or fumes in a quantity sufficient to present danger to human health or the environment, (e) is a cyanide or sulphide bearing waste which, when exposed to pH conditions between two and 12.5, can generate toxic gases, vapours or fumes in a quantity sufficient to present danger to human health or the environment, (f) is capable of detonation or explosive reaction if it is subjected to a strong initiating source or if heated under confinement, (g) is readily capable of detonation or explosive decomposition or reaction at standard temperature and pressure, or (h) is a Class 1 Explosive within the meaning of section 2.9 of the Transportation of Dangerous Goods Regulations made under the Transportation of Dangerous Goods Act, 1992 (Canada); “receiver” means the operator of any facility to which waste is transferred by a carrier; “Registry” has the same meaning as in the Resource Recovery and Circular Economy Act, 2016; “regulated mixed anaerobic digestion facility” means a mixed anaerobic digestion facility that, (a) is regulated under Part IX.1 of Ontario Regulation 267/03 (General) made under the Nutrient Management Act, 2002, and (b) is not subject to an environmental compliance approval issued in respect of an activity mentioned in subsection 27 (1) of the Act; “scavenging” means the uncontrolled removal of reusable material from waste at a waste disposal site; “severely toxic waste” means, (a) a waste that contains a contaminant listed as a severely toxic contaminant in Schedule 3 at a concentration greater than one part per million, (b) a mixture of a waste referred to in clause (a) and any other waste or material, or (c) a waste derived from a waste referred to in clause (a), unless the waste that is derived from the waste referred to in clause (a) is produced in accordance with an environmental compliance approval that states that, in the opinion of the Director, the waste that is produced in accordance with the approval does not have characteristics similar to the characteristics of severely toxic waste referred to in clause (a); “site” means one property and includes nearby properties owned or leased by the same person where passage from one property to another involves crossing, but not travelling along, a public highway; “soil mixture” includes a mixture of soil and liquids, sludges or solids, where, (a) the mixture cannot be separated by simple mechanical removal processes; and (b) based on visual inspection, the volume of the mixture is made up primarily of soil or other finely divided material that is similar to soil; “specimen collection centre” has the same meaning as in the Laboratory and Specimen Collection Centre Licensing Act; “stationary refrigerant waste” means refrigerant that is not mobile refrigerant waste and that is removed from an air-conditioning unit, heat pump, refrigeration or freezer unit; “stationary refrigerant waste collector” means a stationary refrigerant waste management system that collects stationary refrigerant waste it has removed from equipment in which refrigerant is used; “stationary refrigerant waste recycler” means a stationary refrigerant waste management system that receives stationary refrigerant waste from other stationary refrigerant waste management systems and recycles it; “subject waste” means, (a) liquid industrial waste, (b) hazardous waste, and (b.1) waste that was characteristic waste but that has been treated so that it is no longer characteristic waste, if the waste may not be disposed of by land disposal under subsection 79 (1), but does not include waste described in subsection (3); “thermal treatment” includes incineration, gasification, pyrolysis or plasma arc treatment; “thermal treatment site” means a waste disposal site where thermal treatment is used; “total waste disposal volume” means, for a landfilling site, the maximum volume of waste, including the volume of any daily or intermediate cover, to be deposited at the site in the space extending from the base of the waste fill zone or the top of any engineered facilities located on the base of the site to the bottom of the final cover; “Toxicity Characteristic Leaching Procedure” means the Toxicity Characteristic Leaching Procedure, Method 1311, that appears in United States Environmental Protection Agency Publication SW-846 entitled “Test Methods for Evaluating Solid Waste, Physical/Chemical Methods”, as amended from time to time, or a test method that the Director has approved in writing as equivalent; “transfer” means physical transfer of possession; “transfer station” means a waste disposal site used for the purpose of transferring waste from one vehicle to another for transportation to another waste disposal site; “treatment code” means a code listed as a treatment code in Schedule 7; “vehicle” includes a rail car; “vehicle sewage holding tank” means a device permanently mounted in or on a vehicle to receive in-vehicle sewage produced in the vehicle; “waste battery recovery facility” means a site at which intact waste batteries are received for recovery of battery components and at which no disposal of intact waste batteries or of recovered battery components takes place; “waste biomass” means organic matter that is derived from a plant or animal, that is available on a renewable basis and that is, (a) waste from harvesting or processing agricultural products or forestry products, (b) waste resulting from the rendering of animals or animal by-products, (c) solid or liquid material that results from the treatment of wastewater generated by a manufacturer of pulp, paper, recycled paper or paper products, including corrugated cardboard, (d) waste from food processing and preparation operations, or (e) woodwaste; “waste electrical and electronic equipment” has the same meaning as in Ontario Regulation 389/16 (Waste Electrical and Electronic Equipment) made under the Waste Diversion Transition Act, 2016; “waste fill zone” means the three-dimensional zone in which waste is disposed of by landfilling; “waste generation facility” means those facilities, equipment and operations that are involved in the production, collection, handling or storage of waste at a site; “waste transportation system” means those facilities, equipment and operations that are involved in transporting waste beyond the boundaries of a site or from site to site; “waste-derived fuel” means waste that, (a) is hazardous waste, liquid industrial waste, waste described in clause (p), (q), (r), (s), (t) or (u) of the definition of “hazardous waste” or waste described in clause (d) of the definition of “liquid industrial waste”, (b) contains not more than 5 milligrams per kilogram arsenic, not more than 2 milligrams per kilogram cadmium, not more than 10 milligrams per kilogram chromium, not more than 50 milligrams per kilogram lead, not more than 2 milligrams per kilogram PCBs (as defined in Regulation 362 of the Revised Regulations of Ontario, 1990) and not more than 1,500 milligrams per kilogram total halogens, (c) has a flash point of at least 38° Celsius as determined by the Tag Closed Cup Tester (ASTM D-56-79), the Setaflash Closed Cup Tester (ASTM D-3243-77 or ASTM D-3278-78), the Pensky-Martens Closed Cup Tester (ASTM D-93-79) or an equivalent test method approved by the Director, (d) has a quality as fuel not worse than commercially available low grade fuel, and (e) is located at or destined for a waste-derived fuel site, where it will be wholly utilized as a fuel or fuel supplement in a combustion unit; “waste-derived fuel site” means a waste disposal site where waste-derived fuel is wholly utilized as a fuel or fuel supplement in a combustion unit used principally for functions other than waste management and the site may include blending or bulking facilities but may not include facilities for treatment or processing of waste-derived fuel generated off the site; “woodwaste” means waste, (a) that is wood or a wood product, including tree trunks, tree branches, leaves and brush, (b) that is not contaminated with chromated copper arsenate, ammoniacal copper arsenate, pentachlorophenol or creosote, and (c) from which easily removable hardware, fittings and attachments, unless they are predominantly wood or cellulose, have been removed, but does not include, (d) an upholstered article, or (e) an article to which a rigid surface treatment is affixed or adhered, unless the rigid surface treatment is predominantly wood or cellulose; “woodwaste combustor site” means a waste disposal site where woodwaste is subject to thermal treatment or wholly utilized as a fuel or fuel supplement in a combustion unit. R.R.O. 1990, Reg. 347, s. 1; O. Reg. 240/92, s. 1; O. Reg. 501/92, s. 1; O. Reg. 555/92, s. 1; O. Reg. 105/94, s. 1; O. Reg. 190/94, s. 1; O. Reg. 512/95, s. 1; O. Reg. 157/98, s. 1; O. Reg. 460/99, s. 1; O. Reg. 558/00, s. 1 (1-11); O. Reg. 501/01, s. 1; O. Reg. 323/02, s. 1; O. Reg. 461/05, s. 1; O. Reg. 102/07, s. 1 (1-6); O. Reg. 280/07, s. 1; O. Reg. 292/07, s. 1; O. Reg. 395/07, s. 1; O. Reg. 217/08, s. 1 (1); O. Reg. 110/09, s. 1; O. Reg. 336/09, s. 1; O. Reg. 337/09, s. 1; O. Reg. 234/11, s. 1 (1-13); O. Reg. 283/12, s. 1; O. Reg. 334/13, s. 1; O. Reg. 302/14, s. 1 (1-4); O. Reg. 372/15, s. 1; O. Reg. 86/16, s. 1 (1-3); O. Reg. 391/16, s. 1; O. Reg. 408/19, s. 1 (1, 2); O. Reg. 324/22, s. 1; O. Reg. 105/24, s. 1. (1.0.1) For the purposes of clause (b) of the definition of “agricultural waste” in subsection (1), one of the following criteria must be met for waste from a sewage works to be excluded from the definition of “agricultural waste”: 1. Section 53 of the Ontario Water Resources Act applies to the sewage works. 2. The sewage works is for the management of GNF and the following criteria are met: i. Section 53 of the Ontario Water Resources Act does not apply to the sewage works under clause 53 (6) (a) of that Act or section 3.3 of Ontario Regulation 525/98 (Approval Exemptions) made under that Act. ii. Ontario Regulation 300/14 (Greenhouse Nutrient Feedwater) made under the Nutrient Management Act, 2002 does not apply to the management of the GNF under subsection 1 (3) of that regulation. O. Reg. 302/14, s. 1 (5). (1.1) For the purpose of better understanding the definition of “engineered facility” in subsection (1), the following things are examples of common engineered facilities, if they are intended to be functional elements or features of a landfilling site for more than five years: 1. Berms. 2. Drainage ditches. 3. Liners. 4. Covers. 5. Pumps. 6. Facilities to detect, monitor, control, collect, redirect or treat leachate, surface water or ground water. 7. Facilities to detect, monitor, control, collect, redirect, treat, utilize or vent landfill gas. O. Reg. 217/08, s. 1 (2). (2) For the purpose of this Regulation, a waste is derived from a hazardous waste if it is produced from the hazardous waste by blending, stabilization, processing, treatment or disposal. O. Reg. 558/00, s. 1 (12). (3) The definition of “subject waste” in subsection (1) does not include the following wastes: 1. Waste from the servicing of motor vehicles at a retail motor vehicle service station or service facility if, i. there is a written agreement for the collection and other management of such waste with the owner or operator of a waste management system, and ii. the collection or other management of such waste, A. is authorized by an environmental compliance approval, or B. has been prescribed for the purposes of subsection 20.21 (1) of the Act and a registration under Part II.2 of the Act is in effect. 2. Intact waste batteries destined for a waste battery recovery facility. 3. Common mercury waste destined for a common mercury waste recovery facility. 4. Waste electrical and electronic equipment that is intact and is destined for a site at which it is to be processed for the recovery of materials. 5. Printed circuit boards that are waste, are intact and are destined for a site at which they are to be processed for the recovery of materials. 6. Waste from, i. a nursing home under the Nursing Homes Act, ii. a home under the Homes for the Aged and Rest Homes Act, iii. a home for special care under the Homes for Special Care Act, iv.

the professional office of a member of the Royal College of Dental Surgeons of Ontario, or v. the professional office of a member of the College of Physicians and Surgeons of Ontario. 7. Excess soil that is liquid soil, unless the liquid soil is hazardous waste. O. Reg. 102/07, s. 1 (7); O. Reg. 234/11, s. 1 (14); O. Reg. 408/19, s. 1 (3); O. Reg. 120/25, s. 1. (4) For the purposes of paragraph 1 of subsection 1 (3), the servicing of motor vehicles does not include the management of end-of-life vehicles. O. Reg. 86/16, s. 1 (4). Designation and Exemption of Wastes 2. (1) The following are designated as wastes: 1. Dust suppressant. 2. Inert fill. 3. Processed organic waste. 4. Material that consists solely of waste from one or more of the categories set out in Schedule 1, 2 or 3 of Ontario Regulation 101/94 and that either, i. has been separated from other kinds of waste at the source of the material, or ii. comes from a waste disposal site. 5. Rock fill or mill tailings from a mine. 6. Waste-derived fuel. 7. Hazardous waste. 8. Hauled liquid industrial waste. 9. Used tires that have not been refurbished for road use. 10. Stationary refrigerant waste. 11. Mobile refrigerant waste. 12. Woodwaste. 13. Municipal waste. 14. Residue from an industrial, manufacturing or commercial process or operation, if the residue leaves the site where the process or operation is carried on. 15. Hauled sewage. 16. Used lubricating oil. 17. GNF. 18. End-of-life vehicles. O. Reg. 555/92, s. 2; O. Reg. 105/94, s. 2 (1); O. Reg. 128/98, s. 1; O. Reg. 157/98, s. 2; O. Reg. 280/07, s. 2; O. Reg. 302/14, s. 2; O. Reg. 86/16, s. 2. (2) The following materials from the time they leave a construction site or a demolition site are designated wastes: 1. Brick. 2. Corrugated cardboard. 3. Concrete. 4. Drywall. 5. Steel. 6. Wood. O. Reg. 105/94, s. 2 (2). (3) A designation set out in subsection (2) does not apply to material leaving a construction site or demolition site that is being delivered, (a) to the vendor of the material for resale as construction material; (b) to permanent premises of the person undertaking the construction or the person on whose behalf the construction is undertaken, for use as construction material by or for the person; or (c) to permanent premises of the person undertaking the demolition or the person on whose behalf the demolition is undertaken, for use as construction material by or for the person. O. Reg. 105/94, s. 2 (2). 3. (1) The following wastes are exempted from Part V of the Act and this Regulation: 1. Agricultural wastes. 2. Inedible material within the meaning of Ontario Regulation 31/05 (Meat) made under the Food Safety and Quality Act, 2001. 2.1 Any material that is condemned or derived from a carcass at a registered establishment within the meaning of the Meat Inspection Act (Canada). 3. Dead farm animals within the meaning of Ontario Regulation 106/09 (Disposal of Dead Farm Animals) made under the Nutrient Management Act, 2002 or regulated dead animals within the meaning of Ontario Regulation 105/09 (Disposal of Deadstock) made under the Food Safety and Quality Act, 2001. 4. Revoked: O. Reg. 157/98, s. 3. 5. Inert fill. 6. Rock fill or mill tailings from a mine. 7. Material set out in subsection (2). R.R.O. 1990, Reg. 347, s. 3; O. Reg. 105/94, s. 3 (1); O. Reg. 157/98, s. 3; O. Reg. 110/09, s. 2 (1). (2) The material referred to in paragraph 7 of subsection (1) is any of the following: 1. Municipal waste, hazardous waste or liquid industrial waste, other than used or shredded or chipped tires, if, i. the waste is transferred by a generator for direct transportation to a site to be wholly used at the site in an ongoing agricultural, commercial, manufacturing or industrial process or operation that, A. is used principally for functions other than waste management, and B. does not involve combustion or land application of the waste, or ii. the waste is not processed organic waste from a composting facility or excess soil and the waste is transferred by a generator for direct transportation to a site, A. to be promptly packaged for retail sale to meet a realistic market demand, or B. to be offered for retail sale to meet a realistic market demand. 2. Municipal waste, consisting solely of waste from a single category of waste set out in Schedule 1, 2 or 3 of Ontario Regulation 101/94, transferred by a generator and destined for, i. a waste disposal site that, but for the exemption in section 5 of Ontario Regulation 101/94, would be a municipal waste recycling site to which Part IV of that regulation applies and that is located at a manufacturing establishment that uses all the output, other than residues, of the site, or ii. a site for use at the site in an ongoing agricultural, commercial, manufacturing or industrial process or operation used principally for functions other than waste management if the process or operation does not involve combustion or land application of the waste. 3. Residue remaining after metal is recovered from wire and cable and transferred by a generator for direct transportation to a site at which it will be processed for recovery of metal and plastic using a process that does not involve combustion of the residue or any part of the residue. 4. Chipped wood, other than chipped painted wood, chipped treated wood or chipped laminated wood, intended for use as ground cover. 5. Waste wood, other than painted wood, treated wood or laminated wood, transferred by a generator and destined for a site at which it is to be chipped for eventual use as ground cover. 6. Pickle liquor transferred by a generator for direct transportation to a site at which it is to be wholly utilized as a treatment chemical in, i. a sewage works that is subject to the Ontario Water Resources Act, i.1 a sewage works outside Ontario, if the utilization of pickle liquor for this purpose is acceptable to the environmental regulatory authority in the jurisdiction where the sewage works is located, or ii. a wastewater treatment facility that discharges into a sanitary sewer. 7. Solid photographic waste that contains silver, including spent chemical recovery cartridges that contain silver, transferred by a generator and destined for a site at which it is to be processed for recovery of silver. 8. Waste paint or waste coatings transferred by a generator and destined for a site at which the waste is to be used in an ongoing manufacturing process for the production of paint or coatings, if the process does not involve combustion of the waste and the paint or coatings that are produced are not used as fuel. 9. Emission control dust from the primary production of steel in electric furnaces, if the dust is transferred by a generator for direct transportation to a site at which it is to be used as a feedstock in an ongoing high temperature metal recovery process in a rotary kiln, flame reactor, electric furnace, plasma arc furnace, slag reactor, industrial furnace or combination of a rotary hearth furnace and electric furnace. 10. Spent activated carbon transferred by a generator for direct transportation to a site at which it is to be used in a process to reactivate activated carbon. 11. Metal bearing waste, other than lead acid batteries or aqueous waste, that is transferred by a generator for direct transportation to a smelter at which the waste is to be used as a feedstock in an ongoing operation for the recovery of metal, including waste that, for the purpose of being used as a feedstock, is processed through size reduction, blending, calcining, roasting, sintering, drying, pelletizing, cleaning, leaching or separation of solids from liquids, but not including waste that, for the purpose of being used as a feedstock, is processed in any other manner. 12. Printed circuit boards that are waste and that are transferred by a generator and destined for a smelter at which they are to be used as a feedstock in an ongoing operation for the recovery of metal. 13. Waste that is to be processed and used at the same site where it is generated, if, i. neither the processing nor the use of the waste involves combustion or land application of the waste, and ii. the waste is not PCB waste, soil or a soil mixture. 14. Waste biomass transferred by a generator and destined for a site at which it is to be used as a feedstock in the production of ethanol or biodiesel, whether or not it is processed before it is used as a feedstock and whether or not it is processed before it is received at the site at which it is to be used as a feedstock. 15. Crumb rubber recovered from used, chipped or shredded tires and destined for use as a feedstock in the production of rubber products other than fuel products. 16. Waste glass that is to be used as aggregate in pipe bedding or in the subsurface of roads or parking areas. 17. Waste asphalt pavement transferred by a generator for direct transportation to, i. a site at which it is to be used as construction aggregate, or ii. a site at which waste asphalt pavement is processed for use as construction aggregate and at which no disposal of waste or processed waste takes place. 18. Waste asphalt pavement transferred by a generator for direct transportation to a site at which waste asphalt pavement is stored for use as construction aggregate, if, i. the waste asphalt pavement is stored at least 30 metres away from the nearest watercourse, lake or pond, or there are engineered works in place to prevent the waste from having any adverse effect on any watercourse, lake or pond, and ii. the waste asphalt pavement is stored at, A. a construction area for not more than 120 days, B. a permanent place of business for a person who is in the business of construction, C. a pit or quarry for which a permit or licence has been issued under the Aggregate Resources Act, D. a road works yard owned by a municipality or the Crown in right of Ontario, or E. a place that is at least 100 metres from the nearest dwelling. 19. Waste asphalt shingles transferred by a generator and destined for a site at which they will be used as aggregate or surface layer in the construction of walkways for pedestrian use, roads or parking areas, if, before being used for that purpose, the shingles are processed at a site at which the only processing that occurs is sorting, size reduction and the removal of other wastes from the shingles. 20. Organic waste from food processing and preparation operations or operations for the sale or distribution of food, if, i. the waste is transferred by a generator and destined for a site at which the waste will be used in an ongoing agricultural, commercial, manufacturing or industrial process or operation, whether or not it is processed before it is used in the process or operation and whether or not it is processed before it is received at the site at which it will be used in the process or operation, and ii. the agricultural, commercial, manufacturing or industrial process or operation does not involve combustion or land application of the waste. 21. Anaerobic digestion output that is intended for application on agricultural land as nutrient, i. if it was generated by a regulated mixed anaerobic digestion facility, or ii. if the anaerobic digestion materials did not contain sewage biosolids or human body waste and at least 50 per cent, by volume, of the total amount of anaerobic digestion materials were on-farm anaerobic digestion materials. 22. Manure, paunch manure or used animal bedding transferred by a generator for direct transportation to a farm operation at which it is to be used to improve the growing of crops, whether or not it is processed at the operation before it is used to improve the growing of crops. 23. Solid waste plant material that is, i. generated from crops that have not been processed, or that have been processed without any use of chemicals, other than food grade chemicals used only to clean the crops or the surrounding processing area and equipment, and ii. transferred by a generator for direct transportation to a farm operation at which it is to be used to improve the growing of crops, whether or not it is processed at the operation before it is used to improve the growing of crops. 24. Composting material or cured compost if it is transferred by a disposal facility that is operating under a licence issued under the Food Safety and Quality Act, 2001. 25. Processed organic waste from a composting facility, if the waste meets the requirements for Category AA or Category A compost in Part II of the document published by the Ministry entitled “Ontario Compost Quality Standards”, as amended from time to time, originally dated July 25, 2012 and available on a website of the Government of Ontario and through the Ministry’s Public Information Centre. 26. Revoked: O. Reg. 283/12, s. 2 (3). O. Reg. 105/94, s. 3 (2); O. Reg. 128/98, s. 2 (1); O. Reg. 461/05, s. 2; O. Reg. 102/07, s. 2 (1); O. Reg. 395/07, s. 2 (1); O. Reg. 110/09, s. 2 (2); O. Reg. 336/09, s. 2; O. Reg. 283/12, s. 2; O. Reg. 372/15, s. 2; O. Reg. 777/20, s. 1, O. Reg. 237/25, s. 1. (3) Despite subsection (1), material that is referred to in subparagraph 1 i or paragraph 6, 9, 10 or 11 of subsection (2) is exempt from Part V of the Act and this Regulation only if the carrier has in his or her possession while transporting the material a document from the owner or operator of the site to which the material is being transported that, (a) indicates that the owner or operator of the site to which the material is being transported agrees to accept the material; (b) specifies the use that will be made of the material; and (c) if the paragraph of subsection (2) that refers to the material refers to an ongoing process or operation, stipulates that the process or operation is ongoing at the time the material is being transported. O. Reg. 102/07, s. 2 (2). (3.0.1) Despite subsection (1), material that is referred to in paragraph 2, 2.1 or 3 of subsection (1) or paragraph 24 of subsection (2) is exempt from Part V of the Act and this Regulation unless it is transferred to a waste disposal site that is operating under an environmental compliance approval. O. Reg. 110/09, s. 2 (3); O. Reg. 234/11, s. 2. (3.0.2) Despite subsection (1), material that is referred to in paragraph 1, 2, 2.1 or 3 of subsection (1) or paragraph 22, 23 or 24 of subsection (2) is not exempt from section 29 of the Act. O. Reg. 110/09, s. 2 (3). (3.1) Despite subsection (1), material that is referred to in paragraph 7 or 8 of subsection (2) is exempt from Part V of the Act and this Regulation only if, (a) every carrier has in his or her possession while transporting the material a document from the owner or operator of the site to which the material is destined that, (i) indicates that the owner or operator of the site to which the material is destined agrees to accept the material, (ii) specifies the use that will be made of the material, and (iii) if the material is referred to in paragraph 8 of subsection (2), stipulates that the manufacturing process referred to in that paragraph is ongoing at the time the material is being transported; and (b) the owner or operator of every site to which the material is delivered and at which the material is collected, handled, stored or transferred before reaching the site to which the material is destined has in his or her possession while collecting, handling, storing or transferring the material a document from the owner or operator of the site to which the material is destined that, (i) indicates that the owner or operator of the site to which the material is destined agrees to accept the material, (ii) specifies the use that will be made of the material, and (iii) if the material is referred to in paragraph 8 of subsection (2), stipulates that the manufacturing process referred to in that paragraph is ongoing at the time the material is being collected, handled, stored or transferred. O. Reg. 102/07, s. 2 (2). (3.2) If a waste referred to in paragraph 13 of subsection (2) is one of the following types of waste, any residue from the processing of the waste shall be deemed, for the purposes of this Regulation, to be a waste derived from a waste referred to in clause (a) of the definition of that type of waste in subsection 1 (1): 1. Acute hazardous waste chemical. 2. Hazardous industrial waste. 3. Hazardous waste chemical. 4. Severely toxic waste. O. Reg. 102/07, s. 2 (2). (3.3) Paragraph 20 of subsection (2) does not apply to organic waste from food processing and preparation operations or operations for the sale or distribution of food, if the waste is transferred by a generator and destined for a site at which the waste will be subject to anaerobic digestion, composting or any other process or operation that results in the production of material intended for land application. O. Reg. 395/07, s. 2 (2). (4) In subsection (2), “ground cover” means, (a) mulch, (b) landscaping material, or (c) surfacing material for, (i) trails or walkways for pedestrian use, (ii) trails or paths for use by livestock or other animals, (iii) pens or enclosures for livestock or other animals, (iv) playgrounds, (v) parking areas, or (vi) private roads. O. Reg. 128/98, s. 2 (2). Waste Disposal Sites and Waste Management Systems 4. Revoked: O. Reg. 105/94, s. 4. 5. (1) The following waste disposal sites are exempt from Part V of the Act and this Regulation: 1. On-site incinerators at the site of a veterinary hospital. 2. On-site garbage grinders. 3. Revoked: O. Reg. 86/16, s. 3. 4. Incinerators at the site of a crematorium within the meaning of the Cemeteries Act. 5. Regulated mixed anaerobic digestion facilities. R.R.O. 1990, Reg. 347, s. 5 (1); O. Reg. 395/07, s. 3; O. Reg. 86/16, s. 3. (2) Subsection 27 (1) of the Act does not apply in respect of a dust suppression site if, (a) the site has been designated in an environmental compliance approval in respect of establishing and operating a dust suppression waste management system; and (b) the site is established and operated in accordance with the approval. O. Reg. 234/11, s. 3. (3) Revoked: O. Reg. 555/92, s. 4. (4) No person shall use waste oil as a dust suppressant. R.R.O. 1990, Reg. 347, s. 5 (4). 5.0.1 (1) In this section, “municipal waste pilot project site” means a waste disposal site, other than a landfilling site or dump, where municipal waste is processed or disposed of primarily to, (a) assist in the design of technology for processing or disposing of municipal waste, (b) assess the merits of a technology for processing or disposing of municipal waste, or (c) demonstrate the merits of a technology for processing or disposing of municipal waste. O. Reg. 234/11, s. 4. (2) Subject to subsection (3), this section applies to, (a) an application for an environmental compliance approval for the use, operation, establishment, alteration, extension or enlargement of a municipal waste pilot project site; and (b) an application to amend a term or condition described in subsection (5). O. Reg. 234/11, s. 4. (3) Subsection (2) applies to an application if, (a) the applicant gives the Director a written notice that, (i) specifically mentions this section, and (ii) requests that this section apply; and (b) the Director is satisfied that not more than 75 tonnes of municipal waste will be processed or disposed of at the site on any day. O. Reg. 234/11, s. 4. (4) If an environmental compliance approval is issued on an application described in subsection (2), (a) the operator of the municipal waste pilot project site shall promptly notify the Director in writing of the date that municipal waste is first received at the site in accordance with the environmental compliance approval; and (b) the operator of the municipal waste pilot project site shall ensure that not more than 75 tonnes of municipal waste are processed or disposed of at the site on any day. O. Reg. 234/11, s. 4. (5) An environmental compliance approval that is issued on an application described in clause (2) (a) must contain a term or condition that prohibits the operation of the municipal waste pilot project site after the third anniversary of the date that municipal waste is first received at the site, or after such earlier date as is specified in the environmental compliance approval. O. Reg. 234/11, s. 4. (6) Subject to subsections (8) and (9), the Director may, on application, alter the term or condition referred to in subsection (5) if the Director is satisfied that the amendment is necessary to, (a) assist in the design of technology for processing or disposing of municipal waste; (b) assess the merits of a technology for processing or disposing of municipal waste; or (c) demonstrate the merits of a technology for processing or disposing of municipal waste. O. Reg. 234/11, s. 4. (7) The Director is not required to consider an application to alter the term or condition referred to in subsection (5) if, (a) the application is seeking the first alteration of the term or condition; and (b) the application is made less than half way through the period between the date that municipal waste is first received at the site and the date after which the term or condition prohibits the operation of the municipal waste pilot project site. O. Reg. 234/11, s. 4. (8) An alteration of a term or condition under subsection (6) shall not extend the period during which the municipal waste pilot project site may be operated for more than 12 months. O. Reg. 234/11, s. 4. (9) An alteration of a term or condition under subsection (6) shall not extend the period during which the municipal waste pilot project site may be operated beyond the fifth anniversary of the date that municipal waste is first received at the site. O. Reg. 234/11, s. 4. 5.0.2 A waste disposal site is exempt from Part V of the Act and from this Regulation if, (a) it is a NASM plan area, as defined in Ontario Regulation 267/03 (General) made under the Nutrient Management Act, 2002; and (b) it satisfies the requirements of section 8.3 of that regulation. O. Reg. 336/09, s. 3. 5.1 (1) Subsection 27 (1) of the Act does not apply in respect of an end-of-life vehicle waste disposal site if the following criteria are met: 1. The only management of end-of-life vehicles at the site is, i. the removal of parts from end-of-life vehicles for reuse, and ii. the collection, handling, transportation, storage and transfer of end-of-life vehicles. 2. No more than two end-of-life vehicles are received at the site in any 365-day period. 3. No more than 10 end-of-life vehicles are stored at the site at any one time. O. Reg. 86/16, s. 4 (1). (2) Subsection 27 (1) of the Act does not apply in respect of an end-of-life vehicle waste disposal site if the following criteria are met: 1. The only management of end-of-life vehicles at the site is the collection, handling, transportation, storage and transfer of end-of-life vehicles. 2. Each end-of-life vehicle managed at the site is not stored or handled at the site for more than 180 days. O. Reg. 86/16, s. 4 (1). (3) If an environmental compliance approval is not required with respect to an end-of-life vehicle waste disposal site as a result of the application of subsection (1) or (2), sections 40 and 41 of the Act do not apply in respect of that site. O. Reg. 86/16, s. 4 (1). (4) Subsection 27 (1) of the Act and section 16 of this Regulation do not apply in respect of a waste management system if the following criteria are met: 1. The waste management system is a waste transportation system. 2. The only waste management done by the waste management system is the collection, handling, transportation and transfer of end-of-life vehicles. O. Reg. 86/16, s. 4 (1). (5) No person shall shear, crush or shred an end-of-life vehicle, or cause or permit the shearing, crushing or shredding of an end-of-life vehicle, unless all of the following have been removed from the vehicle: 1. Batteries. 2. Battery cable connectors that contain lead. 3. Electrical switches that contain mercury. 4. Fluids, as defined in Ontario Regulation 85/16 (Registrations under Part II.2 of the Act - End-of-life Vehicles) made under the Act. 5. Tires. 6. Tire weights that contain lead. 7. Asbestos waste. 8. Any other materials set out in a document entitled “Materials to be removed from end-of-life vehicles prior to shredding, crushing or shearing” dated March 7, 2016, as amended from time to time, and available on a website of the Government of Ontario. O. Reg. 86/16, s. 4 (2). (6) A person who removes one or more items listed in subsection (5) from an end-of-life vehicle shall, if there are no items listed in subsection (5) left in the end-of-life vehicle after the removal, complete and issue a certificate with respect to the end-of-life vehicle or a shipment of end-of-life vehicles that includes the following information: 1. If the person completing the certificate is the operator of an end-of-life vehicle waste disposal site in respect of which a registration under Part II.2 of the Act is in effect, the registration number that appears on the confirmation of registration in respect of the activity. 2. If the person completing the certificate is the operator of an end-of-life vehicle waste disposal site in respect of which an environmental compliance approval has been issued under Part II.1 of the Act, the number appearing on the environmental compliance approval. 3. If the person completing the certificate is the operator of a waste disposal site outside of Ontario, the address of the site and the number of any applicable approval. 4. The contact information of the person completing the certificate, including the person’s name, business address, telephone number and email address, if any. 5. A statement from the person completing the certificate confirming that there are no items listed in subsection (5) left in the end-of-life vehicle. O. Reg. 86/16, s. 4 (2). (7) A person referred to in subsection (5) may rely upon a certificate respecting an end-of-life vehicle or a shipment of end-of-life vehicles that is completed in accordance with subsection (6) as confirmation that all of the items listed in subsection (5) have been removed, unless the person has reason to believe that one or more listed items have not been removed. O. Reg. 86/16, s. 4 (2). (8) An electronic or paper copy of a certificate completed in accordance with subsection (6) must be retained for at least two years, (a) by the person who completed and issued the certificate at the location where the item was removed; and (b) by the person who received the certificate at the location where the end-of-life vehicle was shredded, crushed or sheared. O. Reg. 86/16, s. 4 (2). 5.2 (1) In this section, “service area”, with respect to a landfilling site, means the geographical area from which the site is permitted, under an environmental compliance approval, to receive municipal waste. O. Reg. 234/11, s. 6. (2) A municipality that owns or operates a landfilling site is exempt from section 27 of the Act with respect to increasing the service area of the site if the additional area from which the site will receive municipal waste is, (a) within the boundaries of the local municipality in which the site is located or, if the upper tier municipality in which the local municipality is located is exercising the power to provide landfilling sites for the local municipality, within the boundaries of that upper tier municipality; (b) within the boundaries of the municipality that owns or operates the site; (c) within the boundaries of an area that is not organized as a municipality and that abuts the municipality that owns or operates the site; or (d) within the boundaries of a separated municipality that abuts the municipality that owns or operates the site. O. Reg. 234/11, s. 6. (3) A municipality that owns or operates a landfilling site that has been filled is exempt from section 27 of the Act with respect to increasing the service area of another landfilling site that it owns and operates if, (a) the municipality relied on an exemption under this section to expand the service area of the filled site or to increase the rate at which municipal waste was received at the filled site; and (b) the additional area from which the other landfilling site will receive municipal waste is part or all of the area from which the filled site received municipal waste. O. Reg. 234/11, s. 6. (4) A person, other than a municipality, who owns or operates a landfilling site is exempt from section 27 of the Act with respect to increasing the service area of the site if, (a) the additional area from which the site will receive municipal waste is within the boundaries of a municipality from which it already receives municipal waste; (b) the municipality referred to in clause (a) is a local municipality or an upper tier municipality that is exercising the power to provide landfilling sites for the local municipality; and (c) the site has an environmental compliance approval that includes terms or conditions establishing a periodic quantity limit for deliveries of waste to the landfilling site. O. Reg. 234/11, s. 6. (5) An increase in the service area to which subsection (2), (3) or (4) applies is exempt from being the subject matter of a hearing under subsection 20.15 (1) of the Act. O. Reg. 234/11, s. 6. (6) An increase in the service area of a landfilling site that is owned or operated by a person other than a municipality is exempt from being the subject matter of a hearing under subsection 20.15 (1) of the Act if, (a) the additional area from which the site will receive municipal waste is within the boundaries of a municipality from which it already receives municipal waste; (b) the municipality referred to in clause (a) is a local municipality or an upper tier municipality that is exercising the power to provide landfilling sites for the local municipality; (c) the site has an environmental compliance approval; (d) the Director imposes a term or condition establishing a periodic quantity limit for deliveries of waste to the site; and (e) the periodic quantity limit is equivalent to an estimate based on existing terms or conditions defining a service area for the site or on historic deliveries to the site. O. Reg. 234/11, s. 6. (7) An increase in the rate at which municipal waste may be received at a landfilling site owned or operated by a municipality from areas within its service area is exempt from being the subject matter of a hearing under subsection 20.15 (1) of the Act. O. Reg. 234/11, s. 6. 6. (1) For the purposes of subsection (3), (a) each tire weighing less than twelve kilograms is one tire unit; (b) each tire weighing twelve kilograms or more is the number of tire units that results from dividing twelve into the number of kilograms that the tire weighs; and (c) each twelve kilograms of chipped or shredded tires is a tire unit. R.R.O. 1990, Reg. 347, s. 6 (1). (2) Steel that has been separated from other components of tires in the process of chipping or shredding tires shall not be counted for the purposes of clause (1) (c). R.R.O. 1990, Reg. 347, s. 6 (2). (3) Section 27 of the Act does not apply in respect of a used tire site if, (a) the total number of tire units at the site is less than 5,000; (b) the total volume of the piles of tire units at the site is less than 300 cubic metres; and (c) used, chipped or shredded tires are not subject to thermal treatment or buried at the site. O. Reg. 183/92, s. 1; O. Reg. 555/92, s. 5 (1); O. Reg. 102/07, s. 5. (4) Despite subsection (3), the only persons exempted from section 40 of the Act for depositing waste at a used tire site described in subsection (3) are persons belonging to one of the following classes: 1. The owner of the land on which the site is located. 2. A person acting with the written permission of the owner of the land on which the site is located. 3. The operator of a motor vehicle service station acting in the ordinary course of the service station business, in the case of a site that is accessory to the station. 4. A person acting with the permission of the operator of a motor vehicle service station and in the ordinary course of the service station business, in the case of a site that is accessory to the station. O. Reg. 183/92, s. 1; O. Reg. 555/92, s. 5 (2). (5) Revoked: O. Reg. 183/92, s. 1. 7. Section 27 of the Act does not apply to vehicle sewage holding tanks. O. Reg. 157/98, s. 4. 8. (1) The following waste management systems are exempt from Part V of the Act and this Regulation: 1. Individual collection systems. 2. Marine craft waste disposal systems. R.R.O. 1990, Reg. 347, s. 8 (1). (2) Revoked: O. Reg. 461/05, s. 4. (3) Section 27 of the Act does not apply in respect of trucks for hauling used tires. R.R.O. 1990, Reg. 347, s. 8 (3). (3.1) Subject to subsection (3.2), sections 27, 40 and 41 of the Act do not apply in respect of trucks for hauling off-farm anaerobic digestion materials listed in Schedule 1 or 2A to Ontario Regulation 267/03 (General) made under the Nutrient Management Act, 2002 to a waste disposal site that, pursuant to paragraph 5 of subsection 5 (1), is exempt from Part V of the Act and this Regulation. O. Reg. 395/07, s. 4; O. Reg. 509/21, s. 1. (3.2) Trucks for hauling off-farm anaerobic digestion materials to a waste disposal site referred to in subsection (3.1) are exempt from sections 27, 40 and 41 of the Act only if every carrier has in his or her possession while transporting the materials a document from the owner or operator of the waste disposal site that indicates that the owner or operator of the site agrees to accept the materials. O. Reg. 395/07, s. 4. (4) Sections 27, 40 and 41 of the Act do not apply in respect of a waste management system or waste disposal site, if the only management of waste done by the system or at the site is the collection, handling, transportation, storage or transfer of, (a) waste that consists of, (i) waste electrical and electronic equipment that is intact, or (ii) printed circuit boards, and that is transferred by a generator and is destined for a site at which the waste is to be processed for the recovery of materials; (b) intact waste batteries that are transferred by a generator and are destined for a waste battery recovery facility; or (c) common mercury waste that is transferred by a generator and is destined for a common mercury waste recovery facility. O. Reg. 102/07, s. 6; O. Reg. 337/09, s. 3. (5) Despite clauses (4) (b) and (c), a waste management system or waste disposal site for the collection, handling, transportation, storage or transfer of waste referred to in those clauses is exempt from sections 27, 40 and 41 of the Act only if, (a) every carrier has in his or her possession while transporting the waste a document from the owner or operator of the waste battery recovery facility or common mercury waste recovery facility that indicates that the owner or operator of the facility agrees to accept the waste; and (b) the owner or operator of every site at which the waste is collected, handled, stored or transferred before reaching the waste battery recovery facility or common mercury waste recovery facility has in his or her possession while collecting, handling, storing or transferring the material a document from the owner or operator of the waste battery recovery facility or common mercury waste recovery facility that indicates that the owner or operator of the facility agrees to accept the waste. O. Reg. 102/07, s. 6. (6) Sections 27, 40 and 41 of the Act do not apply in respect of a waste disposal site if, (a) the only management of waste done at the waste disposal site is the collection, handling, storage, transfer or processing of woodwaste; (b) none of the woodwaste is stored at the waste disposal site for more than 18 months; (c) the woodwaste is transferred by a generator and is destined for one or more woodwaste combustor sites; (d) the owner or operator of the waste disposal site has in his or her possession, while collecting, handling, storing, transferring or processing woodwaste, a document from the owner or operator of each woodwaste combustor site to which the woodwaste is destined that indicates that, (i) the owner or operator of the woodwaste combustor site agrees to accept the woodwaste, and (ii) the woodwaste will be used at the woodwaste combustor site principally for functions other than waste disposal; and (e) no more woodwaste is stored at the waste disposal site than is reasonably capable of being subject to thermal treatment or wholly utilized as a fuel or fuel supplement during a period of six months at the woodwaste combustor sites to which the woodwaste is destined. O. Reg. 102/07, s. 6. (7) Sections 27, 40 and 41 of the Act do not apply in respect of a waste management system if, (a) the only management of waste done by the waste management system is the collection, handling, transportation, storage, transfer or processing of woodwaste; (b) none of the woodwaste is stored at waste disposal sites that are part of the waste management system for more than 18 months; (c) the woodwaste is transferred by a generator and is destined for one or more woodwaste combustor sites; (d) the owner or operator of every waste disposal site that is part of the waste management system has in his or her possession, while collecting, handling, storing, transferring or processing woodwaste, a document from the owner or operator of each woodwaste combustor site to which the woodwaste is destined that indicates that, (i) the owner or operator of the woodwaste combustor site agrees to accept the woodwaste, and (ii) the woodwaste will be used at the woodwaste combustor site principally for functions other than waste disposal; and (e) no more woodwaste is stored at waste disposal sites that are part of the waste management system than is reasonably capable of being subject to thermal treatment or wholly utilized as a fuel or fuel supplement during a period of six months at the woodwaste combustor sites to which the woodwaste is destined. O. Reg. 102/07, s. 6. (8) If, pursuant to subsection (6) or (7), sections 27, 40 and 41 of the Act do not apply in respect of a waste disposal site or waste management system, the owner and the operator of the waste disposal site or waste management system shall ensure that all woodwaste that is transported from the waste disposal site or by the waste management system is transported to, (a) a woodwaste combustor site that uses the woodwaste principally for functions other than waste disposal; or (b) a waste disposal site or waste management system that, pursuant to subsection (6) or (7), is also exempt from sections 27, 40 and 41 of the Act. O. Reg. 102/07, s. 6. (9) Sections 27, 40 and 41 of the Act do not apply in respect of a waste disposal site if, (a) the only management of waste done at the waste disposal site is the collection, handling, storage, transfer or processing of woodwaste; and (b) the site is operated by the holder of a land use permit issued under the Public Lands Act that authorizes the collection, handling, storage transfer or processing of woodwaste at the site. O. Reg. 102/07, s. 6. 9. The standards, procedures and requirements set out in this Regulation do not apply to the extent that terms and conditions in an environmental compliance approval issued in respect of an activity mentioned in subsection 27 (1) of the Act impose different standards, procedures or requirements. R.R.O. 1990, Reg. 347, s. 9; O. Reg. 234/11, s. 7. 10. No person shall use, operate or establish a waste management system or waste disposal site or any part of either of them except in accordance with the applicable prescribed standards. R.R.O. 1990, Reg. 347, s. 10. Standards for Waste Disposal Sites 11. The following are prescribed as standards for the location, maintenance and operation of a landfilling site: 1. Access roads and on-site roads shall be provided so that vehicles hauling waste to and on the site may travel readily on any day under all normal weather conditions. 2. Access to the site shall be limited to such times as an attendant is on duty and the site shall be restricted to use by persons authorized to deposit waste in the fill area. 3. Drainage passing over or through the site shall not adversely affect adjoining property and natural drainage shall not be obstructed. 4. Drainage that may cause pollution shall not, without adequate treatment, be discharged into watercourses. 5. Waste shall be placed sufficiently above or isolated from the maximum water table at the site in such manner that impairment of groundwater in aquifers is prevented and sufficiently distant from sources of potable water supplies so as to prevent contamination of the water, unless adequate provision is made for the collection and treatment of leachate. 6. Where necessary to isolate a landfilling site and effectively prevent the egress of contaminants, adequate measures to prevent water pollution shall be taken by the construction of berms and dykes of low permeability. 7. Where there is a possibility of water pollution resulting from the operation of a landfilling site, samples shall be taken and tests made by the owner of the site to measure the extent of egress of contaminants and, if necessary, measures shall be taken for the collection and treatment of contaminants and for the prevention of water pollution. 8. The site shall be located a reasonable distance from any cemetery. 9. Adequate and proper equipment shall be provided for the compaction of waste into cells and the covering of the cells with cover material. 10. Where climatic conditions may prevent the use of the site at all times, provisions shall be made for another waste disposal site which can be used during such periods. 11. Where required for accurate determination of input of all wastes by weight, scales shall be provided at the site or shall be readily available for use. 12. All waste disposal operations at the site shall be adequately and continually supervised. 13. Waste shall be deposited in an orderly manner in the fill area, compacted adequately and covered by cover material by a proper landfilling operation. 14. Procedures shall be established for the control of rodents or other animals and insects at the site. 15. Procedures shall be established, signs posted, and safeguards maintained for the prevention of accidents at the site. 16. The waste disposal area shall be enclosed to prevent entry by unauthorized persons and access to the property shall be by roadway closed by a gate capable of being locked. 17. A green belt or neutral zone shall be provided around the site and the site shall be adequately screened from public view. 18. Whenever any part of a fill area has reached its limit of fill, a final cover of cover material shall be placed on the completed fill and such cover shall be inspected at regular intervals over the next ensuing period of two years and where necessary action shall be taken to maintain the integrity and continuity of the cover materials. 19. Scavenging shall not be permitted. R.R.O. 1990, Reg. 347, s. 11. 11.1 (0.1) In this section, “Section 39 Director” means a Director appointed under section 5 of the Act for the purposes of section 39 of the Act as that section read immediately before it was repealed. O. Reg. 234/11, s. 8. (1) The owner and the operator of a landfilling site described in subsection (2) shall ensure that on or before June 30, 2009 a written report is submitted to the Section 39 Director respecting, (a) the design, operation, maintenance and monitoring of facilities for the collection, and for the burning or use, of landfill gas generated by the site during site operation and following site closure; and (b) if any of the facilities referred to in clause (a) already exist, the improvements, if any, that can be made to those facilities to increase the amount of landfill gas generated by the site that can be collected, and burned or used, and the date by which the improvements can be made and implemented. O. Reg. 217/08, s. 2; O. Reg. 337/09, s. 4. (2) This section applies to a landfilling site that meets the following criteria: 1. The site accepts only municipal waste for disposal. 2. On or after June 30, 2009, the site will landfill waste under a certificate of approval or provisional certificate of approval issued under Part V of the Act. 3. On or after June 30, 2009, the site will have a total waste disposal volume of more than 1.5 million cubic metres. 4. A written report has not been required to be prepared with respect to the site under subsection 15 (1) of Ontario Regulation 232/98 (Landfilling Sites) made under the Act. O. Reg. 217/08, s. 2. (3) This section does not apply to a landfilling site associated with forest products operations, such as the operations of a lumber mill, sawmill, pulp mill or similar facility, if the waste deposited at the site is produced by the forest products operations and is predominantly solid, non-hazardous process waste, such as woodwaste, effluent treatment solids, hog fired boiler ash, recycling process rejects, lime mud, grits or dregs. O. Reg. 217/08, s. 2. (4) This section does not apply to a landfilling site if the only waste landfilled at the site is coal ash. O. Reg. 217/08, s. 2. (5) This section does not apply to a landfilling site if a written report is submitted to the Section 39 Director before June 30, 2009 showing that the nature and quantity of landfill gas generated by the site is not likely to be of significant concern to the Director, based on the following factors: 1. The characteristics of the site. 2. The type of waste to be deposited. 3. The rate at which waste is deposited at the site. O. Reg. 217/08, s. 2. (6) This section does not apply to a landfilling site that meets the following criteria: 1. The site operates under a certificate of approval or provisional certificate of approval issued under Part V of the Act. 2. The certificate of approval or provisional certificate of approval permits the use of facilities for the collection, and for the burning or use, of landfill gas generated by the site during site operation but does not require that some or all of those facilities be used. 3. The site has in operation facilities that are not required by the certificate of approval or provisional certificate of approval for the collection, and for the burning or use, of landfill gas generated by the site during site operation. 4. The owner or the operator of the site gives the Section 39 Director a written notice that, i. specifically mentions this subsection, and ii. requests that this section not apply. O. Reg. 217/08, s. 2. 11.2 (0.1) In this section, “Section 39 Director” means a Director appointed under section 5 of the Act for the purposes of section 39 of the Act as that section read immediately before it was repealed. O. Reg. 234/11, s. 9 (1). (1) If section 11.1 does not apply to a landfilling site because the criteria listed in subsection 11.1 (6) are met, the owner and the operator of the site shall ensure that, on or before June 30, 2009, a written report is submitted to the Section 39 Director, (a) identifying the areas of the site where facilities for the collection, and for the burning or use, of landfill gas generated by the site during site operation are in operation and for which there is no requirement under the certificate of approval or provisional certificate of approval under which the site operates; (b) describing the design and operation of facilities for the collection, and for the burning or use, of landfill gas generated by the site during site operation and following site closure in the areas of the site that are identified in clause (a);

(c) respecting the design, operation, maintenance and monitoring of facilities for the collection, and for the burning or use, of landfill gas generated by the site during site operation and following site closure in the areas of the site that are not identified in clause (a); and (d) if any of the facilities referred to in clause (c) already exist, respecting the improvements, if any, that can be made to those facilities to increase the amount of landfill gas generated by the site that can be collected, and burned or used, and the date by which the improvements can be made and implemented. O. Reg. 217/08, s. 2; O. Reg. 337/09, s. 5. (2) The owner and the operator of a landfilling site for which a written report was required to be submitted under subsection (1) shall ensure that, on or before June 30, 2016, a written report is submitted to the Director respecting, (a) the design, operation, maintenance and monitoring of the facilities for the collection, and for the burning or use, of landfill gas generated by the site during site operation and following site closure; and (b) if any of the facilities referred to in clause (a) already exist, the improvements, if any, that can be made to those facilities to increase the amount of landfill gas generated by the site that can be collected, and burned or used, and the date by which the improvements can be made and implemented. O. Reg. 217/08, s. 2; O. Reg. 234/11, s. 9 (2). 11.3 (1) Subject to subsection (2), the owner and the operator of a landfilling site to which section 11.1 or 11.2 applies shall ensure that the following facilities and improvements to the facilities are in operation for the collection, and for the burning or use, of landfill gas generated by the site during site operation and following site closure: 1. If section 11.1 applies, the facilities referred to in clause 11.1 (1) (a) and any improvements identified under clause 11.1 (1) (b). 2. If section 11.2 applies, the facilities referred to in clause 11.2 (1) (c) and any improvements identified under clause 11.2 (1) (d). O. Reg. 217/08, s. 2. (2) If, after a report was submitted under subsection 11.1 (1) or 11.2 (1), facilities other than facilities referred to in subsection (1) have been required as a condition in an environmental compliance approval, the owner and the operator shall ensure that the facilities required by the Director are in operation for the collection, and for the burning or use, of landfill gas generated by the site during site operation and following site closure. O. Reg. 234/11, s. 10. (3) This section applies to a portion of a waste fill zone in a landfilling site to which section 11.1 applies or in an area of a landfilling site to which section 11.2 applies that is not identified in clause 11.2 (1) (a) if, at any time on or after December 31, 2010, (a) the portion of the zone has reached its maximum capacity; or (b) no further waste has been deposited in the portion of the zone during the preceding six months. O. Reg. 217/08, s. 2. 11.4 (0.1) In this section, “Section 39 Director” means a Director appointed under section 5 of the Act for the purposes of section 39 of the Act as that section read immediately before it was repealed. O. Reg. 234/11, s. 11 (1). (1) The owner and the operator of a landfilling site described in subsection (4) shall ensure that for 2009 and every subsequent year, an annual report is submitted to the Director on or before June 1 of the following year. O. Reg. 217/08, s. 2; O. Reg. 234/11, s. 11 (2). (2) The report required under subsection (1) shall be in writing and shall include the following with respect to the facilities for the collection, and for the burning or use, of landfill gas generated by the landfilling site during site operation and following site closure: 1. A statement of the total landfill gas volume collected by the facilities at the site during the year. 2. A statement of the percentage of the volume described in paragraph 1 that was methane gas. 3. A statement of the reduction in methane emissions from the landfilling site associated with the burning or use of landfill gas during the year, expressed in units of tonnes of carbon dioxide equivalent and based on a global warming potential of 21 for methane gas. 4. A description of how sound scientific or engineering principles have been used to support the statements required by paragraphs 1, 2 and 3. 5. All calculations and information that support the statements required by paragraphs 1, 2 and 3. O. Reg. 217/08, s. 2. (3) The report required for 2009 under subsection (1) shall include the information described in subsection (2) only for the period that begins on June 30, 2009 and ends on December 31, 2009. O. Reg. 217/08, s. 2. (4) This section applies to a landfilling site that meets the following criteria: 1. The site accepts only municipal waste for disposal. 2. On or after June 30, 2009, the site landfills waste and is subject to an environmental compliance approval. 3. On or after June 30, 2009, the site has a total waste disposal volume of more than 1.5 million cubic metres. O. Reg. 217/08, s. 2; O. Reg. 234/11, s. 11 (3). (5) This section does not apply to a landfilling site associated with forest products operations, such as the operations of a lumber mill, sawmill, pulp mill or similar facility, if the waste deposited at the site is produced by the forest products operations and is predominantly solid, non-hazardous process waste, such as woodwaste, effluent treatment solids, hog fired boiler ash, recycling process rejects, lime mud, grits or dregs. O. Reg. 217/08, s. 2. (6) This section does not apply to a landfilling site if the only waste landfilled at the site is coal ash. O. Reg. 217/08, s. 2. (7) This section does not apply to a landfilling site for which a written report has been submitted to the Section 39 Director under subsection 11.1 (5). O. Reg. 217/08, s. 2. (8) This section ceases to apply to a landfilling site if the Director amends an environmental compliance approval to which the site is subject to state that the nature and quantity of landfill gas generated by the site is not of significant concern to the Director. O. Reg. 217/08, s. 2; O. Reg. 234/11, s. 11 (4). 11.5 (1) On request of the Director, the owner or the operator who is required to submit a report under section 11.1, 11.2 or 11.4 shall provide further information with respect to the subject matter of the report. O. Reg. 217/08, s. 2; O. Reg. 234/11, s. 12 (1). (2) The information requested under subsection (1) shall be provided to the Director by a date set by the Director at the time of the request. O. Reg. 217/08, s. 2; O. Reg. 234/11, s. 12 (2). 12. The following are prescribed as standards for the location, maintenance and operation of a thermal treatment site: 1. The location of the thermal treatment site shall be selected so as to reduce the effects of nuisances such as dust, noise and traffic. 2. Fly-ash that is hazardous waste and that results from the incineration of waste that is neither hazardous waste nor liquid industrial waste shall be kept separate from incinerator ash and disposed of or otherwise dealt with separately from incinerator ash. 3. Fly-ash that is hazardous waste and that results from the incineration of waste that is neither hazardous waste nor liquid industrial waste shall only be disposed of at, i. Revoked: O. Reg. 337/09, s. 6. ii. a landfilling site authorized to accept fly-ash that is hazardous waste and that results from the incineration of waste that is neither hazardous waste nor liquid industrial waste by the terms of, A. an environmental compliance approval issued after the 1st day of January, 1990, or B. an amendment to an environmental compliance approval made after the 1st day of January, 1990. 4. The thermal treatment equipment shall be located, i. so that it is accessible for the transportation of wastes thereto without nuisance, ii. taking into account meteorological considerations to minimize environmental effects, and iii. so that the services and utilities required for the operation of the thermal treatment equipment are available, including facilities for the disposal of residue and of quenching and scrubbing water. 5. The design and capacity of the thermal treatment equipment shall be of a type and size adequate to efficiently process the quantities of waste that may be expected, so that a minimum volume of residue is obtained, the putrescible materials remaining as residue are reduced to a minimum and a minimum of air pollution results. 6. The following equipment shall be provided as necessary for particular applications: i. Scales for the accurate determination of the input of all wastes by weight. ii. A storage pit or other storage facilities. iii. A crane or other means of removing waste from the pit or other storage facilities. iv. Means of controlling dusts and odours. v. Such instruments as may be necessary for the efficient operation of the thermal treatment equipment. 7. The thermal treatment site shall include an unloading area properly enclosed and of sufficient size for the intended operation. 8. Access roads shall be provided for vehicles hauling waste to the thermal treatment site. 9. On-site fire protection shall be provided and, where possible, arrangements shall be made with a fire department or municipality for adequate fire fighting services in case of an emergency. 10. Scavenging shall not be permitted. R.R.O. 1990, Reg. 347, s. 12; O. Reg. 102/07, s. 7; O. Reg. 337/09, s. 6; O. Reg. 234/11, s. 13. 12.1 Revoked: O. Reg. 512/95, s. 2. 13. The following are prescribed as standards for the location, maintenance and operation of a dump: 1. The fill area shall not be subject to flooding and shall be so located that no direct drainage leads to a watercourse. 2. The site shall be at least one-quarter of a mile from the nearest dwelling. 3. The site shall be at least two hundred yards from the nearest public road. 4. The site shall be at least 100 feet from any watercourse, lake or pond. 5. The site shall not be on land covered by water. 6. Signs shall be posted stating requirements for the operation of the dump, including measures for the control of vermin and insect infestation. 7. The site shall be so located and operated as to reduce to a minimum the hazards resulting from fire. 8. The operator of a dump shall apply such cover material at such intervals as is necessary to prevent harm or material discomfort to any person. 9. Scavenging shall not be permitted. R.R.O. 1990, Reg. 347, s. 13. 14. (1) No dump shall be established, altered, enlarged or extended in Ontario. O. Reg. 337/09, s. 7 (1). (2), (3) Revoked: O. Reg. 337/09, s. 7 (2). 14.0.1 If hazardous waste is being handled, stored, treated or disposed of at a waste disposal site or transferred to a waste disposal site, no person shall cause or permit the hazardous waste to be mixed, blended, bulked or in any other way intermingled with any other waste or material, unless the mixing, blending, bulking or other intermingling is in accordance with an environmental compliance approval issued in respect of the waste disposal site. O. Reg. 461/05, s. 5; O. Reg. 234/11, s. 14. 14.1 The following are prescribed as standards for the location, maintenance and operation of waste disposal sites for hauled sewage: 1. A person shall not apply hauled sewage in any manner that permits it to enter a watercourse or drainage ditch. 2. A person shall not apply hauled sewage in any manner that results in runoff leaving the site. 3. If the operator of a proposed site is not the owner of the land on which the site is to be located, the operator must, before applying for approval to engage at the site in an activity mentioned in subsection 27 (1) of the Act, obtain written authorization from the owner for the proposed use of the site. O. Reg. 157/98, s. 5; O. Reg. 234/11, s. 15. 14.2 (1) Subject to subsection (3), no person shall cause or permit waste from a portable toilet to be applied to land or otherwise deposited at a site except, (a) at a waste disposal site that is subject to an environmental compliance approval permitting the temporary storage of hauled sewage and from which the hauled sewage is not subsequently removed and disposed of except in accordance with this section; (b) at a waste disposal site that is subject to an environmental compliance approval permitting the disposal of hauled sewage for drying and requiring the dried residue to be periodically removed and disposed of at a waste disposal site approved to accept the dried residue; (c) at a landfilling site that is subject to an environmental compliance approval for the final disposal of hauled sewage; (d) at a sewage works that is subject to an environmental compliance approval permitting the receipt of sanitary sewage or hauled sewage; or (e) at a site that is subject to an environmental compliance approval permitting the processing of waste and which processes waste in a manner that ensures that the waste meets all of the following requirements after it has been processed: (i) the concentration of Escherichia coli (E. coli) in the waste is not more than 2x106 colony forming units per gram of total solids (dry weight), (ii) the concentration in the waste of each metal listed in the Table to this section is not more than the maximum concentration set out for that metal in the Table, (iii) the pH value of the waste is not less than 6.0, (iv) the waste has been passed through a screen and contains no more than 0.5 per cent dry weight of plastic objects and no more than 2 per cent dry weight of other non-biodegradable objects, including, but not limited to, glass and metal objects. O. Reg. 326/03, s. 1; O. Reg. 234/11, s. 16 (1-5). (2) Subsection (1) applies despite anything contained in a certificate of approval or a provisional certificate of approval that was issued before this section comes into force. O. Reg. 326/03, s. 1. (3) No person shall cause or permit waste from a portable toilet to be disposed of at an organic soil conditioning site unless, (a) the organic soil conditioning site is subject to an environmental compliance approval permitting the spreading or application of treated waste from a portable toilet; (b) the waste has been treated so that the concentration of Escherichia coli (E. coli) is not more than 2x106 colony forming units per gram of total solids (dry weight); (c) the concentration in the waste of each metal listed in the Table to this section is not more than the maximum concentration set out for that metal in the Table; (d) the pH value of the treated waste is not less than 6.0; and (e) the waste has been passed through a screen and contains no more than 0.5 per cent dry weight of plastic objects and no more than 2 per cent dry weight of other non-biodegradable objects, including, but not limited to, glass and metal objects. O. Reg. 326/03, s. 1; O. Reg. 234/11, s. 16 (6). TABLE Item Metal Maximum Permissible Concentration (In mg/kg Of Solids, Dry Weight) 1. Arsenic 170 2. Cadmium 34 3. Cobalt 340 4. Chromium- 2,800 5. Copper 1,700 6. Mercury 11 7. Molybdenum 94 8. Nickel 420 9. Lead 1,100 10. Selenium 34 11. Zinc 4,200 O. Reg. 326/03, s. 1. 15. The following are prescribed as standards for the location, maintenance and operation of an organic soil conditioning site: 1. The site shall be so located that it is an adequate distance from any watercourse, as determined by the land slope, to prevent direct surface drainage to the watercourse. 2. The site shall be at least 300 feet from the nearest individual dwelling. 3. The site shall be at least 1,500 feet from any area of residential development. 4. The site shall be so located that the maximum level of the ground water table at the site is at a sufficient distance below the surface to prevent the impairment of ground water in aquifers as determined by the permeability of the soil. 5. The site shall be at least 300 feet from any water wells. 6. No processed organic waste shall be applied to the site during any period in which conditions are such that surface runoff is likely to occur taking into account land slope, soil permeability and the climatic conditions of the area. 7. The site shall be established only on land that is, or is intended to be, used for pasture, fallow or the growing of forage crops, i. during the current growing season, or ii. where application of the processed organic waste is made sometime after the current growing season, to the end of the subsequent growing season. 8. Berms and dykes of low permeability shall be constructed on the site where necessary to isolate the site and effectively prevent the egress of contaminants. R.R.O. 1990, Reg. 347, s. 15. 16. (1) The following are prescribed as standards for the operation of a waste management system: 1. All waste collection vehicles and waste carriers shall be so constructed as to enable waste to be transferred safely and without nuisance from storage containers to the vehicle. 2. Bodies of waste collection vehicles and waste carriers shall be so constructed as to withstand abrasion and corrosion from the waste. 3. Bodies of waste collection vehicles and waste carriers shall be leakproof and covered where necessary to prevent the emission of offensive odours, the falling or blowing of waste material from the vehicles or the release of dust or other air-borne materials that may cause air pollution. 4. Valves that are part of a waste transportation vehicle used for transporting liquid industrial waste or hazardous waste shall have a locking mechanism and shall be locked when the vehicle contains the waste and the driver of the vehicle is not in attendance. 5. Whenever liquid industrial waste or hazardous waste is being transferred to or from a waste transportation vehicle, the driver of the vehicle must be present unless the generator or receiver is present. 5.1 If hazardous waste is being transferred to or from a waste transportation vehicle or is being transported in a waste transportation vehicle, no person shall cause or permit the hazardous waste to be mixed, blended, bulked or in any other way intermingled with any other waste or material, unless, i. the mixing, blending, bulking or other intermingling is in accordance with an environmental compliance approval issued in respect of the receiving facility named in the manifest that is related to the waste transportation vehicle’s load, and the carrier has, accompanying the load, a document from the owner or operator of the receiving facility agreeing to accept the mixed, blended, bulked or otherwise intermingled waste, or ii. the mixing, blending, bulking or other intermingling is done in accordance with an environmental compliance approval issued in respect of a waste transportation system that the waste transportation vehicle is part of. 6. A waste transportation vehicle used for transporting liquid industrial waste or hazardous waste shall be clearly marked with the name and number appearing on the environmental compliance approval that authorizes the transportation. 7. Where a waste transportation vehicle is used for transporting liquid industrial waste or hazardous waste, a copy of the environmental compliance approval that authorizes that transportation shall be kept in the vehicle. 8. A waste transportation vehicle used for transporting liquid industrial waste or hazardous waste shall be constructed, maintained, operated and marked or placarded in accordance with the applicable requirements of the Transportation of Dangerous Goods Act, 1992 (Canada). 9. The driver of a waste transportation vehicle used for the transportation of municipal waste, liquid industrial waste or hazardous waste shall be trained in, i. the operation of the vehicle and waste management equipment, ii. relevant waste management legislation, regulations and guidelines, iii. major environmental concerns pertaining to the waste to be handled, iv. occupational health and safety concerns pertaining to the waste to be handled, and v. emergency management procedures for the wastes to be handled. 10. A waste transportation vehicle used for transporting municipal waste shall be clearly marked with the name and number appearing on the environmental compliance approval that authorizes the transportation. 11. Where a waste transportation vehicle is used for transporting municipal waste, a copy of the environmental compliance approval that authorizes that transportation shall be kept in the vehicle. 12. If the waste management system is used for hauled sewage, the operator of the system shall ensure that every tank used for the transportation of hauled sewage has inscribed in plain view the words “Sewage Waste” in letters that are at least 15 centimetres in height, unless the tank bears a company designation in letters of at least that height that clearly indicates the nature of the contents. 13. If the waste management system is used for hauled sewage, the operator of the system shall ensure that any part of the system that comes into contact with hauled sewage is not used for the collection, handling, treatment, transportation, storage or processing of any material other than hauled sewage or a material approved in writing by the Director. 14. A person shall not discharge or permit the discharge of hauled sewage from a tank that is part of a waste management system to the ground except in accordance with terms and conditions contained in an environmental compliance approval or order. 15. No person shall discharge or permit the discharge of GNF at a waste disposal site for hauled sewage. R.R.O. 1990, Reg. 347, s. 16; O. Reg. 105/94, s. 7 (1); O. Reg. 157/98, s. 6 (1); O. Reg. 461/05, s. 6; O. Reg. 234/11, s. 17 (1-4); O. Reg. 348/12, s. 1; O. Reg. 302/14, s. 3; O. Reg. 324/22, s. 2. (1.1) If a registration under Part II.2 of the Act is in effect in respect of an activity mentioned in paragraph 6 or 10 of subsection (1), those paragraphs do not apply and instead the name and registration number that appears on the confirmation of registration in respect of the activity shall be clearly marked on the vehicle. O. Reg. 120/25, s. 2. (1.2) If a registration under Part II.2 of the Act is in effect in respect of an activity mentioned in paragraph 7 or 11 of subsection (1), those paragraphs do not apply and instead a copy of the confirmation of registration in respect of the activity shall be kept in the vehicle. O. Reg. 120/25, s. 2. (2) Paragraphs 10 and 11 of subsection (1) do not apply, (a) if the vehicle is owned and operated by or operated exclusively for a municipality or the Crown; or (b) if the vehicle is operating as part of a waste management system in respect of which no environmental compliance approval is required. O. Reg. 105/94, s. 7 (2); O. Reg. 234/11, s. 17 (5). (3) Paragraph 13 of subsection (1) does not apply if, (a) the part of the waste management system that came into contact with hauled sewage is not used for the collection, handling, treatment, transportation, storage or processing of hazardous waste, hauled liquid industrial waste or liquids for human or animal consumption; (b) the part of the system that came into contact with hauled sewage is used for the collection, handling, treatment, transportation, storage or processing of other liquid material and the owner or operator of the system obtains every approval required for that purpose; and (c) the part of the system that came into contact with hauled sewage is cleaned, to the satisfaction of any person to whom the other liquid material will be transferred, before that part of the system is used for the collection, handling, treatment, transportation, storage or processing of the other liquid material. O. Reg. 157/98, s. 6 (2). (4) If, pursuant to subsection (3), a part of a waste management system that came into contact with hauled sewage is used for the collection, handling, treatment, transportation, storage or processing of other liquid material, a person shall not use that part of the system again for hauled sewage unless it, and any other part of the system that was contaminated during the collection, handling, treatment, transportation, storage or processing of the other liquid material, has been cleaned to the satisfaction of the Director. O. Reg. 157/98, s. 6 (2). (5) The operator of a waste management system for hauled sewage shall, (a) keep daily records of the premises from which hauled sewage is collected and the amounts of sewage collected from those premises; (b) keep daily records of the disposal site or disposal sites at which hauled sewage is discharged or disposed of and the amounts of hauled sewage discharged or disposed of at those sites; and (c) keep the daily records required by clauses (a) and (b) available for review by the Director, as the Director may require, for a period of at least two years after the calendar year to which the records relate. O. Reg. 157/98, s. 6 (2). 16.1 The following are prescribed as standards for the operation and maintenance of vehicle sewage holding tanks: 1. A person shall not discharge or permit the discharge of effluent from a vehicle sewage holding tank to the surface of the ground or into ground water, surface water, a piped water supply, a well water supply, a watercourse or a drainage ditch. 2. A person shall not discharge or permit the discharge of effluent from a vehicle sewage holding tank except from a place on or part of the tank, or from a piping system connected to the tank, that is designed to discharge effluent. 3. The owner and the operator of a vehicle sewage holding tank shall ensure that insects and animals are prevented from gaining access to sewage in the tank. 4. The owner and the operator of a vehicle sewage holding tank shall ensure that the tank does not discharge micro organisms of intestinal origin into the natural environment in a manner that may be hazardous to human health. 5. The owner and the operator of a vehicle sewage holding tank shall ensure that no gas is discharged into a building or structure from the tank or a piping system connected to the tank except in a manner for which the tank or piping system was designed. 6. The owner and the operator of a vehicle sewage holding tank shall ensure that the tank does not receive any waste other than in-vehicle sewage produced in the vehicle. 7. The owner and the operator of a vehicle sewage holding tank shall ensure that the tank and any piping system connected to the tank are maintained in good operating condition. O. Reg. 157/98, s. 7. Management of Asbestos Waste 17. (1) No person shall manage asbestos waste except in accordance with the following: 1. No person shall cause or permit asbestos waste to leave the location at which it is generated except for the purpose of transporting it, in accordance with paragraph 2, to a waste disposal site, the operator of which has agreed to accept it and has been advised as to its anticipated time of arrival. 2. Asbestos waste transported to a waste disposal site shall, i. be in a rigid, impermeable, sealed container of sufficient strength to accommodate the weight and nature of the waste, or ii. where the asbestos waste is being transported in bulk, be transported by means of a waste management system that is subject to an environmental compliance approval that specifically authorizes the transportation of asbestos waste in bulk. 3. Where a container referred to in subparagraph i of paragraph 2 is a cardboard box, the waste must be sealed in a six-mil polyethylene bag placed within the box. 4. Every container referred to in subparagraph i of paragraph 2 must be free from punctures, tears or leaks. 5. The external surfaces of every container referred to in subparagraph i of paragraph 2 and of every vehicle or vessel used for the transport of asbestos waste must be free from asbestos waste. 6. Both sides of every vehicle used for the transportation of asbestos waste and every container referred to in subparagraph i of paragraph 2 must display thereon in large, easily legible letters that contrast in colour with the background the word “CAUTION” in letters not less than ten centimetres in height and the words: CONTAINS ASBESTOS FIBRES Avoid Creating Dust and Spillage Asbestos May be Harmful To Your Health Wear Approved Protective Equipment. 7. Asbestos waste being transported from the location at which it is generated, i. shall be transported, A. by a driver trained in the management of asbestos waste, B. as directly as may be practicable, to the waste disposal site at which disposal of the asbestos waste is intended to take place, ii. shall not be transferred to a transfer station or other waste disposal site where disposal of the asbestos waste will not take place, but it may be transported to a waste disposal site that is subject to an environmental compliance approval that specifically authorizes acceptance and processing of asbestos waste, iii. shall not be transported with any other cargo in the same vehicle, iv. shall not be transported in a compaction type waste haulage vehicle, v. where it is being transported in cardboard boxes, shall be in an enclosed vehicle, vi. shall be properly secured and covered with a suitable tarpaulin or net if it is transported in a vehicle that is not enclosed, and vii. shall be transported only in vehicles equipped with emergency spill cleanup equipment including a shovel, a broom, wetting agent, protective clothing, a supply of six-mil polyethylene bags, bag closures and personal respiratory equipment. 8. During the transportation or unloading thereof, any asbestos waste that is loose or in a container that is punctured, broken or leaking shall be packaged, immediately on discovery, in a six-mil polyethylene bag. 9. Where containers of asbestos waste are being unloaded, the unloading shall be carried out so that no loose asbestos or punctured, broken or leaking containers of asbestos waste are landfilled. 10. Asbestos waste may be deposited only at locations in a landfilling site that have been adapted for the purpose of receiving asbestos waste or are otherwise suitable for that purpose. 11. Asbestos waste may be deposited at a landfilling site only while the depositing is being supervised by the operator of the site or a person designated by the operator for the purpose and the person supervising is not also operating machinery or the truck involved. 12. Where asbestos waste is deposited, as set out in paragraph 10, at least 125 centimetres of garbage or cover material must be placed forthwith over the deposited asbestos waste in such a manner that direct contact with compaction equipment or other equipment operating on the site is avoided. 13. Every person handling asbestos waste or containers of asbestos waste, supervising the unloading of asbestos waste in bulk or cleaning asbestos waste residues from containers, vehicles or equipment shall wear protective clothing and personal respiratory equipment while so doing. 14. Protective clothing that has been or is suspected of having been in contact with asbestos waste shall be changed at the site of the exposure and either properly disposed of as asbestos waste or washed at the end of the working day. 15. Disposable protective clothing shall not be reused. 16. Every person directly or indirectly involved in the transportation, handling or management of asbestos waste shall take all precautions necessary to prevent asbestos waste from becoming airborne. R.R.O. 1990, Reg. 347, s. 17; O. Reg. 234/11, s. 18. (2) If a registration under Part II.2 of the Act is in effect in respect of an activity mentioned in paragraph 2 of subsection (1), subparagraph 2 ii of that subsection does not apply in respect of the activity. O. Reg. 120/25, s. 3. Waste Generation Facilities 17.1 (1) Sections 27, 40 and 41 of the Act do not apply to a waste generation facility in respect of the activities set out in subsection (2) of this section, to the extent that those activities relate to waste that was produced at the waste generation facility, other than PCB waste. O. Reg. 120/25, s. 4. (2) The following activities are the activities referred to in subsection (1): 1. The production, collection, handling or temporary storage of municipal waste. 2. The production, collection, handling or temporary storage of subject waste. 3. The processing of waste, if the processing does not involve, i. the combustion or land application of municipal waste, hazardous waste or liquid industrial waste, ii. the mixing, blending, bulking or other intermingling of waste or other material with characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed, or iii. the processing of soil, except if the processing is permitted to be carried out under Ontario Regulation 406/19 (On-Site and Excess Soil Management) made under the Act. 4. The processing of municipal waste with on-site thermal treatment equipment that, pursuant to subsection 28 (1) of this Regulation, is exempt from the operation of section 27 of the Act. 5. The processing of characteristic waste or listed waste, if the processing involves the mixing, blending, bulking or other intermingling of waste or other material with the characteristic waste or listed waste, and, i. the processing will, by itself or in conjunction with other processing, permit the land disposal of the characteristic waste or listed waste under section 75, 76, 77, 78 or 79, or ii. the mixed, blended, bulked or otherwise intermingled waste is to be transported to a receiving facility, the mixing, blending, bulking or other intermingling is in accordance with an environmental compliance approval issued in respect of the receiving facility, and the operator of the waste generation facility has, at the waste generation facility, a document from the owner or operator of the receiving facility agreeing to accept the mixed, blended, bulked or otherwise intermingled waste. 6. The processing of waste so that it becomes exempt from Part V of the Act and this Regulation under paragraph 7 of subsection 3 (1). 7. The introduction of waste into, and the processing of waste in preparation for the introduction of the waste into, i. a sewage works that is subject to the Ontario Water Resources Act or that was established before August 3, 1957, or ii. a sewage system regulated under Part 8 of Division B of Ontario Regulation 332/12 (Building Code) made under the Building Code Act, 1992. 8. The packaging or offering of waste for retail sale to meet a realistic market demand, and the processing of waste, if the processing is for the purpose of packaging or offering the waste for retail sale to meet a realistic demand. 9. The transfer to a waste transportation vehicle of, i. municipal waste, or ii. subject waste, other than characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed. 10. The transfer to a waste transportation vehicle of characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed, if the transfer does not involve the mixing, blending, bulking or other intermingling of the characteristic waste or listed waste with any other waste or material. 11. The transfer to a waste transportation vehicle of characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed, if the transfer involves the mixing, blending, bulking or other intermingling of the characteristic waste or listed waste with any other waste or material and, i. the mixing, blending, bulking or other intermingling is in accordance with an environmental compliance approval issued in respect of the receiving facility named in the manifest that is related to the waste transportation vehicle’s load, and the carrier has, accompanying the load, a document from the owner or operator of the receiving facility agreeing to accept the mixed, blended, bulked or otherwise intermingled waste, or ii. the mixing, blending, bulking or other intermingling is done in accordance with an environmental compliance approval issued in respect of a waste transportation system that the waste transportation vehicle is part of. O. Reg. 461/05, s. 7; O. Reg. 102/07, s. 8; O. Reg. 234/11, s. 19; O. Reg. 334/13, s. 2; O. Reg. 408/19, s. 3. (3) Subsection (1) does not apply to a waste generation facility if waste management is the principal function of the waste generation facility. O. Reg. 461/05, s. 7. 17.1.1 Subject to section 27.1, all documents that are required to be submitted through the Registry by this Regulation shall be submitted electronically. O. Reg. 324/22, s. 3. 17.2 If a waste generation facility to which subsection 17.1 (1) applies stores subject waste, the operator and the owner of the facility shall ensure that it is operated in accordance with the following rules: 1. Subject waste must be stored, handled and maintained so as to prevent, i. leaks or spills of the waste, or ii. damage to or deterioration of the container in which the waste is stored. 2. Subject waste must not be stored for a period exceeding 24 months unless, i. an application for approval under Part II.1 of the Act respecting the storage of subject waste by the waste generation facility has been made and has not yet been determined, or ii. an application for a certificate of approval respecting the storage of subject waste by the waste generation facility was made before Part II.1 of the Act came into force and has not yet been determined. 3. The first time that subject waste is stored at the waste generation facility for more than 90 days, a notice, containing the information required in the Manual and in this Regulation, must be submitted through the Registry, within five business days after the 90th day of storage, that, i. describes, as accurately as possible, the nature, amount and location of subject waste stored, or expected to be stored in the future, at the waste generation facility for more than 90 days, and ii. indicates how frequently subject waste is expected to be stored in the future at the waste generation facility for more than 90 days. 4. If notice is submitted under paragraph 3, a notice must be submitted through the Registry setting out, i. any change in the information referred to in paragraph 3, within five business days after the change, or ii. the closure of the waste generation facility, within five business days after the closure. 5. If subject waste is stored at the waste generation facility for more than 90 days, a record must be made of the following information within five business days after the 90th day of storage: i. The name and waste number of the waste. ii. The quantity of the waste. iii. The manner in which the waste is stored. iv. The reasons for storing the waste. v. The anticipated time and manner of disposal of the waste. 6. A record made under paragraph 5 must be updated as often as necessary to ensure that it contains information that is current to within five business days. 7. A record made or updated under paragraph 5 or 6 must be retained at the location where subject waste is stored, or i. the record must be maintained at the head office of the operator or owner of the facility, and ii. an electronic copy of the record must be retained at the location where subject waste is stored. 8. A record made or updated under paragraph 5 or 6 must be retained until the date that the subject waste is no longer stored, and for at least two years after that date. O. Reg. 461/05, s. 7; O. Reg. 337/09, s. 8; O. Reg. 234/11, s. 20; O. Reg. 324/22, s. 4. Generator Registration 18. (1) Every generator who operates a waste generation facility that is involved in the production, collection, handling or storage of subject waste shall submit, through the Registry, a Generator Registration Report that contains the information required in the Manual and this Regulation in respect of the facility before one of the following events, whichever occurs first: 1. The transfer of subject waste from the facility. 2. The passing of 90 days since the first day subject waste was produced, collected or stored at the facility. O. Reg. 324/22, s. 5 (1). (1.1) Subsection (1) applies to waste produced, collected, handled or stored at the waste generation facility that is subject waste and that is characteristic waste or listed waste, even if the waste ceases to be hazardous waste while it is at the facility. O. Reg. 461/05, s. 8 (1). (2) Every Generator Registration Report referred to in subsection (1) or (6) shall comply with the Manual and this Regulation and shall contain the data, analysis and other information necessary to enable the Director to be satisfied of the following: 1. The quality, quantity and nature of the waste. 2. The required treatment for the waste and the planned treatment for the waste. 3. The intended manner and location of the disposal of the waste or, if the waste is not to be disposed, the use to which the waste will be put. 4. Compliance with all applicable legal requirements. O. Reg. 461/05, s. 8 (2); O. Reg. 324/22, s. 5 (2). (3), (4) Revoked: O. Reg. 324/22, s. 5 (3). (5) Revoked: O. Reg. 461/05, s. 8 (3). (6) If there is any change from the information submitted in a Generator Registration Report or a previous supplementary Generator Registration Report, the generator shall submit a supplementary Generator Registration Report, through the Registry, that contains the information required in the Manual and this Regulation within 15 days after the change. O. Reg. 324/22, s. 5 (4). (6.1) A generator who submits a Generator Registration Report or a supplementary Generator Registration Report under this section shall make a record of all data, analysis and other information used in the preparation of the report and shall keep the record at one of the following locations for at least three years after the date subject waste is no longer produced, collected, handled or stored at the waste generation facility: 1. The waste generation facility. 2. The head office of the generator, if an electronic copy of the record may be accessed at the waste generation facility. O. Reg. 324/22, s. 5 (5). (7) No generator shall transfer a particular subject waste from a waste generation facility to a waste transportation system unless, (a) the generator has submitted, through the Registry, a Generator Registration Report and any required supplementary Generator Registration Reports with respect to that facility and that particular subject waste, including the waste number for that particular subject waste; or (b) the generator has been approved under section 27.1 to submit paper forms and, having submitted the required forms in compliance with that section, a generator registration document for that waste generation facility with a waste number for that particular subject waste has been posted on the Registry. O. Reg. 324/22, s. 5 (6). (7.1) Revoked: O. Reg. 324/22, s. 5 (6). (7.2) In all transfers of subject waste under this Regulation, every generator shall use the generator registration number issued in respect of the waste generation facility from which the subject waste is being transferred and the applicable waste numbers set out in the Manual. O. Reg. 501/01, s. 2 (1). (8) Every generator shall keep a record of the subject waste disposed of at the waste generation facility including the name, waste number, quantity and disposition of the waste. R.R.O. 1990, Reg. 347, s. 18 (8). (9) A record referred to in subsection (8) may be disposed of after two years. R.R.O. 1990, Reg. 347, s. 18 (9). (10) Revoked: O. Reg. 461/05, s. 8 (5). (11) Revoked: O. Reg. 324/22, s. 5 (7). (12) In unusual circumstances, such as a spill, a process aberration or upset, or the circumstances described in subsection 22 (2), where a generator discovers that a generator registration number or a waste number is needed to comply with this Regulation in the disposal of subject waste, the Director may assign a generator registration number or accept a waste number identified by the generator. R.R.O. 1990, Reg. 347, s. 18 (12); O. Reg. 234/11, s. 21 (2). (13) Where a generator registration number is assigned under subsection (12), subsection (7) does not apply and subsections (1) and (2) shall be complied with within ninety days. O. Reg. 501/01, s. 2 (2); O. Reg. 324/22, s. 5 (8). (14) Where a waste number is accepted under subsection (12), subsection (7) does not apply and the generator shall submit a supplementary Generator Registration Report respecting the waste for which the waste number was accepted within ninety days. O. Reg. 501/01, s. 2 (2); O. Reg. 324/22, s. 5 (9). (14.1) Revoked: O. Reg. 324/22, s. 5 (10). (15) Revoked: O. Reg. 337/09, s. 9 (4). Manifests — Generator Requirements 19. (1) No generator shall permit subject waste to pass from the generator’s control or to leave the waste generation facility except, (a) by transfer of the subject waste to a waste transportation system that is subject to an environmental compliance approval, or for which a registration under Part II.2 of the Act is in effect, and where the generator has completed a manifest in respect of the waste in accordance with the Manual and this Regulation; or (b) by direct discharge to a sewage works, other than a storm sewer, that is subject to the Ontario Water Resources Act or was established before August 3, 1957, or into a sewage system regulated under Part 8 of Division B of Ontario Regulation 332/12 (Building Code) made under the Building Code Act, 1992. R.R.O. 1990, Reg. 347, s. 19 (1); O. Reg. 460/99, s. 3; O. Reg. 501/01, s. 3; O. Reg. 337/09, s. 10; O. Reg. 234/11, s. 22; O. Reg. 334/13, s. 3; O. Reg. 120/25, s. 5. (2) No generator shall transfer subject waste to a waste transportation system unless the subject waste is so packaged or marked that it meets the transport requirements of the Transportation of Dangerous Goods Act, 1992 (Canada). R.R.O. 1990, Reg. 347, s. 19 (2); O. Reg. 324/22, s. 6. Manifests — Carrier Requirements 20. Every carrier shall, on or before January 31, 2023, dispose of every unused paper manifest that was supplied to the carrier and shall report in writing to the Director the number of each paper manifest disposed of on or before that date. O. Reg. 324/22, s. 7. 20.1 (1) No carrier shall have possession of subject waste in Ontario unless the waste was accepted from a generator and a waste generation facility for which, (a) the generator has submitted, through the Registry, a Generator Registration Report and any required supplementary Generator Registration Reports with respect to that facility and that particular subject waste, including the waste number for that particular subject waste; (b) the generator has been approved under section 27.1 to submit paper forms and, having submitted the required forms in compliance with that section, a generator registration document for that waste generation facility with a waste number for that particular subject waste has been posted on the Registry; or (c) a generator registration number has been assigned or a waste number has been accepted under subsection 18 (12). O. Reg. 324/22, s. 8. (2) Subsection (1) does not apply in respect of subject waste, (a) accepted from a generator to whom section 18 does not apply; or (b) accepted from outside Ontario for the purpose of being transported for transfer to a receiving facility outside Ontario. O. Reg. 501/01, s. 5. 21. (1) No carrier shall have possession of subject waste unless the carrier has, accompanying the waste, a manifest in respect of the waste, with the generator and carrier information completed in accordance with the Manual and this Regulation, except during a transfer while the manifest is being completed by a generator or receiver. R.R.O. 1990, Reg. 347, s. 21 (1); O. Reg. 460/99, s. 4; O. Reg.

324/22, s. 9 (1). (2) For purposes of subsection (1), information in a manifest is not completed in accordance with this Regulation if it contains an obvious error. R.R.O. 1990, Reg. 347, s. 21 (2); O. Reg. 324/22, s. 9 (2). (3) Either of the following shall be sufficient for the purposes of having the manifest accompany the waste under subsection (1): 1. Having a paper copy of the completed generator and carrier information available at all times during which the carrier is in possession of the waste. 2. Having access to an electronic display of the completed generator and carrier information at all times during which the carrier is in possession of the waste. O. Reg. 324/22, s. 9 (3). 22. (1) No carrier shall permit subject waste to pass from the carrier’s control except in accordance with this Regulation. R.R.O. 1990, Reg. 347, s. 22 (1). (2) A carrier, with the specific approval of the Director, may transfer subject waste in Ontario to any of the following in order to alleviate a dangerous situation: 1. Another vehicle in the same waste transportation system. 2. A waste transportation system that is subject to an environmental compliance approval. 3. A waste transportation system for which a registration under Part II.2 of the Act is in effect. 4. A receiving facility. O. Reg. 120/25, s. 6 (1). (3) Where a truckload or less of subject waste has been transferred by a generator to a waste transportation system, the carrier shall, on the day the waste is transferred, transport the waste to the receiving facility named in the manifest related to that load unless the carrier is permitted to do otherwise by subsection (2) or section 27. R.R.O. 1990, Reg. 347, s. 22 (3); O. Reg. 337/09, s. 12. (4) Despite subsection (3), if the receiving facility named in the manifest related to that load is located outside of Ontario, a carrier may transport the waste to the receiving facility on a day subsequent to the day the waste is transferred, if the carrier is temporarily storing the waste in the waste transportation vehicle in accordance with section 12 of Ontario Regulation 119/25 (Registrations under Part II.2 of the Act — Waste Transportation Systems) made under the Act. O. Reg. 120/25, s. 6 (2). Manifests — Transport within Ontario 23. (1) This section applies where a generator transfers subject waste in Ontario to a waste transportation system for transport to a receiving facility in Ontario and, for the purpose of this section, “generator” includes a carrier to whom subsection 22 (2) applies. R.R.O. 1990, Reg. 347, s. 23 (1). (2) No generator shall transfer subject waste to a waste transportation system unless, for each truckload or part thereof transferred, at the time of the transfer, (a) the generator submits, through the Registry, the generator manifest information required in the Manual and this Regulation; and (b) the carrier submits, through the Registry, the carrier manifest information required in the Manual and this Regulation. O. Reg. 324/22, s. 10 (1). (2.1) Revoked: O. Reg. 324/22, s. 10 (1). (3) A carrier may transfer subject waste, (a) with the specific approval of the Director, in order to alleviate a dangerous situation, to, (i) another vehicle of the same waste transportation system, (ii) a waste transportation system that is subject to an environmental compliance approval, (iii) a waste transportation system for which a registration under Part II.2 of the Act is in effect, or (iv) a specified receiving facility as mentioned in clause (b), (c) or (d); (b) to a waste disposal site that is subject to an environmental compliance approval that authorizes acceptance of the waste; (c) with the consent of the owner of the sewage works, to a sewage works in respect of which an environmental compliance approval has been issued and that is not in contravention of the approval; or (d) to a waste-derived fuel site having a combustion unit that is subject to an environmental compliance approval issued in respect of an activity mentioned in section 9 of the Act that authorizes acceptance and combustion of the waste. R.R.O. 1990, Reg. 347, s. 23 (3); O. Reg. 234/11, s. 24 (1-4); O. Reg. 120/25, s. 7. (4) No receiver shall accept subject waste from a carrier under subsection (3) unless, at the time of the transfer, (a) the carrier submits, through the Registry, the carrier manifest information required in the Manual and this Regulation and gives the receiver the number of the manifest on the Registry for that load of waste; and (b) the receiver submits, through the Registry, the receiver manifest information required in the Manual and this Regulation. O. Reg. 324/22, s. 10 (2). (5) The following rules apply with respect to every carrier who is the operator of a waste transportation system that is subject to an environmental compliance approval to operate as a dust suppression waste management system: 1. The carrier may deposit for the purposes of dust suppression, in accordance with the approval, dust suppressant at a dust suppression site designated in the approval. 2. The carrier shall, as quickly as is reasonably possible following completion of the deposit, submit, through the Registry, the receiver manifest information required in the Manual and this Regulation. O. Reg. 324/22, s. 10 (2). (5.1)-(8) Revoked: O. Reg. 324/22, s. 10 (2). Manifests — Transport out of Ontario 24. (1) This section applies where a generator transfers subject waste in Ontario to a waste transportation system for transport to a receiving facility outside Ontario. R.R.O. 1990, Reg. 347, s. 24 (1). (2) No generator shall transfer subject waste to a waste transportation system unless, for each truckload or part thereof transferred, at the time of the transfer, (a) the generator submits, through the Registry, the generator manifest information required in the Manual and this Regulation; and (b) the carrier submits, through the Registry, the carrier manifest information required in the Manual and this Regulation. O. Reg. 324/22, s. 11. (3) No carrier shall transport subject waste out of Ontario destined for a receiving facility outside Ontario unless the carrier has reason to believe the intended receiver is willing to comply with clause 4 (b). O. Reg. 324/22, s. 11. (4) No receiver shall accept subject waste from a carrier unless, at the time of the transfer, (a) the carrier submits, through the Registry, the carrier manifest information required in the Manual and this Regulation and gives the receiver the number of the manifest on the Registry for that load of waste; and (b) the receiver submits, through the Registry, the receiver manifest information required in the Manual and this Regulation. O. Reg. 324/22, s. 11. (4.1) Revoked: O. Reg. 324/22, s. 11. (5) If the carrier is aware that the receiver has not complied with clause 4 (b), the carrier shall notify the Director as soon as reasonably possible of, (a) the number of the manifest; (b) the name of the receiver, if it is not the same as the name of the intended receiver included in the information submitted by the generator under subsection (2); and (c) the date of the transfer to the receiver. O. Reg. 324/22, s. 11. (6)-(10) Revoked: O. Reg. 324/22, s. 11. Manifests — Transport into Ontario 25. (1) This section applies where subject waste is transferred outside Ontario to a waste transportation system for transport to a receiving facility in Ontario. R.R.O. 1990, Reg. 347, s. 25 (1). (2) No carrier shall bring subject waste into Ontario for the purposes of transport to a receiving facility in Ontario unless, for each truckload or part thereof transferred, at the time of the transfer from the generator, (a) the generator submits, through the Registry, the generator manifest information required in the Manual and this Regulation; and (b) the carrier submits, through the Registry, the carrier manifest information required in the Manual and this Regulation. O. Reg. 324/22, s. 12 (1). (3)-(4) Revoked: O. Reg. 324/22, s. 12 (1). (5) A carrier may transfer subject waste, (a) to a waste disposal site that is subject to an environmental compliance approval that authorizes acceptance of the waste; (b) with the consent of the owner of the sewage works, to a sewage works in respect of which an environmental compliance approval has been issued, and that is not in contravention of the approval; or (c) to a waste-derived fuel site having a combustion unit that is subject to an environmental compliance approval in respect of activities mentioned in section 9 of the Act that authorizes acceptance and combustion of the waste. R.R.O. 1990, Reg. 347, s. 25 (5); O. Reg. 234/11, s. 25 (1-3). (6) No receiver shall accept subject waste from a carrier under subsection (5) unless, at the time of the transfer, (a) the carrier submits, through the Registry, the carrier manifest information required in the Manual and this Regulation and gives the receiver the number of the manifest on the Registry for that load of waste; and (b) the receiver submits, through the Registry, the receiver manifest information required in the Manual and this Regulation. O. Reg. 324/22, s. 12 (2). (7) The following rules apply with respect to every carrier who is the operator of a waste transportation system that is subject to an environmental compliance approval to operate as a dust suppression waste management system: 1. The carrier may deposit for the purposes of dust suppression, in accordance with the approval, dust suppressant at a dust suppression site designated in the approval. 2. The carrier shall, as quickly as is reasonably possible following completion of the deposit, submit, through the Registry, the receiver manifest information required in the Manual and this Regulation. O. Reg. 324/22, s. 12 (2). (7.1)-(10) Revoked: O. Reg. 324/22, s. 12 (2). Manifests — Transport through Ontario 26. (1) No carrier shall transport through Ontario subject waste from outside Ontario for transfer to a receiving facility outside Ontario unless the generator has with the waste, for each truckload or portion thereof, a manifest, or a paper copy of an electronic manifest, completed in accordance with the requirements of the jurisdiction issuing the manifest. O. Reg. 501/01, s. 10. (2) Where this section applies, a manifest issued under the Canadian Environmental Protection Act, 1999 (Canada) or an equivalent manifest issued by a Canadian jurisdiction or a Uniform Hazardous Waste Manifest as prescribed by the United States Environmental Protection Agency may be used for purposes of compliance with this Regulation. R.R.O. 1990, Reg. 347, s. 26 (2); O. Reg. 337/09, s. 16. Fees 26.1 The fees due under this Regulation before January 1, 2023 that are payable to the Ministry of Finance continue after that date to be due and payable to the Minister of Finance. O. Reg. 324/22, s. 13 (2). Refusals 27. (0.1) A receiver shall decide whether to accept or refuse to accept a transfer of subject waste within 24 hours after the waste arrives at the receiving facility. O. Reg. 337/09, s. 17. (1) A receiver who refuses to accept a transfer of subject waste shall submit, through the Registry, the refusal report information required in the Manual and this Regulation within one business day after the refusal. O. Reg. 324/22, s. 14 (1). (2) Where a carrier intends to transfer subject waste to a receiving facility and the waste is refused by the intended receiver, the carrier, before attempting to make a different transfer, shall consult and obtain the instructions of the generator, unless written instructions have been provided by the generator in advance and may transfer the waste to a receiving facility indicated in the instructions. R.R.O. 1990, Reg. 347, s. 27 (2). (3) If waste is refused by the intended receiver at the receiving facility and if the carrier cannot conveniently make a different transfer in accordance with this Regulation, the carrier may transfer the unadulterated waste to the waste generation facility set out in the generator information in the applicable manifest and, at the time of the transfer, (a) the carrier shall submit, through the Registry, the information required in the Manual and this Regulation; and (b) the generator shall submit, through the Registry, the receiver manifest information required in the Manual and this Regulation. O. Reg. 324/22, s. 14 (2). (4) Every generator shall accept a transfer of unadulterated subject waste in the circumstances described in subsection (3). R.R.O. 1990, Reg. 347, s. 27 (4). (5)-(6) Revoked: O. Reg. 324/22, s. 14 (3). (7) A waste generation facility is exempt from the requirement of a waste disposal site certificate of approval under section 27 of the Act in respect of an acceptance of waste under this section. R.R.O. 1990, Reg. 347, s. 27 (7). Submission of Information to Registry 27.1 (1) If a person believes that complying with the requirement to submit a document electronically through the Registry will result in undue hardship to that person, the person may submit a request to the Director in accordance with the Manual and this Regulation for approval to submit a paper document instead. O. Reg. 324/22, s. 15. (2) A Director may approve a request under subsection (1) for the person to submit a paper document if, after considering the circumstances of the person, the Director is of the opinion that submitting the document electronically would impose undue hardship on the person. O. Reg. 324/22, s. 15. (3) The Director shall specify, in every written approval provided under subsection (2), the document and the period of time in respect of which the approval applies. O. Reg. 324/22, s. 15. (4) If the Director provides an approval to a person under subsection (2), the person shall, with respect to each paper document to which the approval applies, (a) submit the document in accordance with the Manual; (b) send the document to the person specified in the Manual, who shall electronically submit, through the Registry, the information in the document on behalf of the person who made the request; (c) comply with the procedures and deadlines specified in the Manual with respect to the submission of the document; and (d) keep any records related to the document as required in the Manual and this Regulation. O. Reg. 324/22, s. 15. (5) If a person is authorized to submit manifest information pursuant to an approval under subsection (2), every person who is required to submit information in respect of that manifest shall also use paper. O. Reg. 324/22, s. 15. 27.2 (1) For greater certainty, a generator who is required to submit a document through the Registry may authorize in writing a delegate to submit the document on their behalf. O. Reg. 324/22, s. 15. (2) A written authorization mentioned in subsection (1) must comply with any requirements set out in the Manual. O. Reg. 324/22, s. 15. (3) A generator who has entered into an agreement with a delegate through a written authorization remains responsible for meeting their requirements under this Regulation, including requirements to report, update and ensure the accuracy of all information submitted through the Registry. O. Reg. 324/22, s. 15. (4) The generator and the delegate must retain a copy of the written authorization for the duration of the authorization and for at least two years after the authorization ceases to have effect. O. Reg. 324/22, s. 15. On-Site Thermal Treatment Equipment 28. (1) On-site thermal treatment equipment is exempt from the operation of section 27 of the Act unless the equipment is used to subject hazardous waste or liquid industrial waste to thermal treatment. O. Reg. 102/07, s. 9. (2) Revoked: O. Reg. 234/11, s. 26. (3) This section does not apply to on-site thermal treatment equipment at a woodwaste combustor site or waste-derived fuel site. O. Reg. 102/07, s. 9. Woodwaste Combustor Sites 28.1 (1) Sections 27, 40 and 41 of the Act do not apply to a woodwaste combustor site for residential heating in respect of woodwaste if not more than fifty cubic metres of woodwaste is stored at the woodwaste combustor site at any time. O. Reg. 337/09, s. 18 (1). (2) Sections 27, 40 and 41 of the Act do not apply to a woodwaste combustor site in respect of woodwaste if, (a) none of the woodwaste stored at the woodwaste combustor site is stored there for more than 18 months; and (b) no more woodwaste is stored at the woodwaste combustor site than is reasonably capable of being subject to thermal treatment or wholly utilized as a fuel or fuel supplement during a period of six months at the site. O. Reg. 102/07, s. 10; O. Reg. 337/09, s. 18 (2). (2.1) Subsection (2) does not apply on any day on which more than 100 tonnes of woodwaste are subject to thermal treatment at the site, if the sole purpose of subjecting the woodwaste to thermal treatment is to dispose of it. O. Reg. 102/07, s. 10. (2.2) Subsection (2) does not apply to a woodwaste combustor site at which woodwaste is subject to thermal treatment, if the principal function of the site is waste disposal. O. Reg. 102/07, s. 10. (2.3) Sections 27, 40 and 41 of the Act do not apply to a woodwaste combustor site in respect of woodwaste if, (a) woodwaste is subject to thermal treatment at the woodwaste combustor site and the principal function of the site is waste disposal; (b) not more than 100 tonnes of woodwaste is subject to thermal treatment at the woodwaste combustor site on any day; (c) not more than 500 cubic metres of woodwaste is stored at the woodwaste combustor site at any time; and (d) none of the woodwaste stored at the woodwaste combustor site is stored there for more than six months. O. Reg. 102/07, s. 10; O. Reg. 337/09, s. 18 (3). (3) A woodwaste combustor site is exempt from section 27 of the Act in respect of its use and operation if, (a) the woodwaste combustor site was first put into operation before the 26th day of September, 1992; and (b) immediately before the 26th day of September, 1992, no certificate of approval or provisional certificate of approval under Part V of the Environmental Protection Act was required for the use or operation of the woodwaste combustor site. O. Reg. 555/92, s. 8. (4) A woodwaste combustor site that is exempt under subsection (3) ceases to be exempt if the use or operation of the woodwaste combustor site changes substantially. O. Reg. 555/92, s. 8. (5) A woodwaste combustor site that is exempt under subsection (3) ceases to be exempt at the end of the twelve-month period immediately following the 26th day of September, 1992, if the woodwaste combustor site is in operation on fewer than thirty days during that twelve-month period. O. Reg. 555/92, s. 8. 28.2 Revoked: O. Reg. 234/11, s. 27. Waste-Derived Fuel Sites 28.3 (1) A waste-derived fuel site is exempt from section 27 of the Act if, (a) the only waste-derived fuel utilized at the waste-derived fuel site is waste-derived fuel that is generated at the waste-derived fuel site and has never left the site; and (b) not more than ten tonnes of waste-derived fuel is utilized at the waste-derived fuel site on any day. O. Reg. 555/92, s. 8. (2) A waste-derived fuel site is exempt from section 27 of the Act in respect of its use and operation if, (a) the waste-derived fuel site was first put into operation before the 26th day of September, 1992; and (b) immediately before the 26th day of September, 1992, no certificate of approval or provisional certificate of approval under Part V of the Environmental Protection Act was required for the use or operation of the waste-derived fuel site. O. Reg. 555/92, s. 8. (3) A waste-derived fuel site that is exempt under subsection (2) ceases to be exempt if the use or operation of the waste-derived fuel site changes substantially. O. Reg. 555/92, s. 8. (3.1) A waste-derived fuel site described in subsection 28.6 (1) that is exempt under subsection (2) ceases to be exempt if, (a) the site is altered by the replacement of the combustion unit; (b) the site is altered by an increase in the capacity of the combustion unit or the incorporation of an additional combustion unit; or (c) the site is enlarged or extended. O. Reg. 280/07, s. 3. (4) A waste-derived fuel site that is exempt under subsection (2) ceases to be exempt at the end of the twelve-month period immediately following the 26th day of September, 1992, if the waste-derived fuel site is in operation on fewer than thirty days during that twelve-month period. O. Reg. 555/92, s. 8. 28.4 Revoked: O. Reg. 234/11, s. 27. 28.5 (1) At a waste-derived fuel site, no person shall mix waste that is not waste-derived fuel with any other waste or material, if the material resulting from the mixing is waste-derived fuel. O. Reg. 555/92, s. 8. (2) Subsection (1) does not apply to prohibit the mixing of two or more wastes that are generated at the waste-derived fuel site and have never left the site. O. Reg. 555/92, s. 8. 28.6 (1) No person shall use, operate, establish, alter, enlarge or extend a waste-derived fuel site, or cause or permit the use, operation, establishment, alteration, enlargement or extension of a waste-derived fuel site, if the site includes a combustion unit that is used principally for heating the interior of a building or other enclosed space for the comfort of occupants or for the provision of a suitable temperature for materials, including plant or animal life, in the building or enclosed space. O. Reg. 280/07, s. 4. (2) Subsection (1) does not apply to a waste-derived fuel site that is located in the Territorial District of Algoma, Cochrane, Kenora, Manitoulin, Nipissing, Parry Sound, Rainy River, Sudbury, Thunder Bay or Timiskaming. O. Reg. 280/07, s. 4. (3) Before June 1, 2009, subsection (1) does not apply to a waste-derived fuel site that is in operation on the day this section comes into force, if, on the day this section comes into force, (a) the combustion unit is operating under a certificate of approval that authorizes acceptance and combustion of waste and that was issued under section 9 of the Act before January 11, 2007; (b) the site is used in agriculture; or (c) pursuant to subsection 28.3 (2), the site is exempt from section 27 of the Act in respect of its use and operation. O. Reg. 280/07, s. 4. (4) Subsection (3) ceases to apply to a waste-derived fuel site if, (a) the site is altered by the replacement of the combustion unit; (b) the site is altered by an increase in the capacity of the combustion unit or the incorporation of an additional combustion unit; or (c) the site is enlarged or extended. O. Reg. 280/07, s. 4. Existing Hospital Incinerators 29. (1) Revoked: R.R.O. 1990, Reg. 347, s. 29 (3); See O. Reg. 323/02, s. 2. (2) Revoked: R.R.O. 1990, Reg. 347, s. 29 (3); See O. Reg. 323/02, s. 2. (3) Spent: O. Reg. 323/02, s. 2. (4) All existing hospital incinerators that operated under the authority of subsection (1) or (2) and all hospital incinerators operating under a certificate of approval issued before December 6, 2002 must cease operations on or before December 6, 2003. O. Reg. 323/02, s. 2. (5) All certificates of approval for hospital incinerators issued before this subsection came into force are revoked on December 6, 2003. O. Reg. 323/02, s. 2. Field Operations 29.1 Section 18 does not apply to a generator in respect of subject waste from field operations if the subject waste is destined for a local waste transfer facility. O. Reg. 337/09, s. 19. 29.2 Sections 19 to 26 do not apply to generators, carriers or receivers of subject waste from field operations if the subject waste is destined for a local waste transfer facility. O. Reg. 337/09, s. 19. 29.3 Sections 27, 40 and 41 of the Act do not apply to a local waste transfer facility if, (a) no hazardous waste or liquid industrial waste, other than waste from field operations, is received or stored at the facility; and (b) there is available, at or near the facility, fire-fighting equipment and spill clean-up and containment equipment that is appropriate to the quantities and types of waste at or expected to be at the facility. O. Reg. 337/09, s. 19. 29.4 Sections 27, 40 and 41 of the Act do not apply in respect of a local waste transfer facility if, (a) access to the facility is controlled by gates, fencing, attendants or other security measures; (b) subject to clause (c), any hazardous waste or liquid industrial waste at the facility is stored on an impermeable pad that, (i) is or can be covered to keep out precipitation, and (ii) has curbs, berms, catch basins or other features that are sufficient to prevent hazardous waste or liquid industrial waste from escaping into the natural environment; (c) any syringes or other sharps, and any related waste, at the facility are stored indoors in puncture resistant containers that prevent exposure or spilling of the contents; (d) the locations where hazardous waste, liquid industrial waste and waste described in clause (c) are stored at the facility are readily accessible for inspection, containment of spills and spills clean-up; (e) there is available, at or near the facility, fire-fighting equipment and spill clean-up and containment equipment that is appropriate to the quantities and types of waste at or expected to be at the facility; (f) a written record is kept each time hazardous waste or liquid industrial waste is received and stored at the facility or is transferred from the facility, and the record specifies the nature and quantity of the waste and is retained at the facility for at least two years after the record is made; and (g) written notice that identifies the facility and sets out the facility’s location and the quantities and types of wastes that are at or are anticipated to be at the facility is given to the Director, (i) one month before the facility is established, or (ii) within fifteen days after this section comes into force, in the case of a facility that is in operation when this section comes into force. O. Reg. 337/09, s. 19; O. Reg. 234/11, s. 28. 29.5 Sections 27, 40 and 41 of the Act and section 16 of this Regulation do not apply in respect of a waste management system if, (a) the system is owned or operated by a person who undertakes field operations or a person on whose behalf field operations are undertaken; and (b) the operations of the system are limited to the collection and handling of waste from the field operations referred to in clause (a) and the transportation of the waste to, (i) a local waste transfer facility, or (ii) a waste disposal site that is authorized to receive the waste, if the waste is not subject waste. O. Reg. 337/09, s. 19. Waste from Covid-19 Antigen Point-of-Care Testing 29.6 (1) In this section, “COVID-19 antigen point-of-care testing” means testing that employs a COVID-19 medical device authorized by the Minister of Health (Canada) for point-of-care use and that employs antigen testing technology; “COVID-19 testing waste” means hazardous waste generated by COVID-19 antigen point-of-care testing and includes any hazardous waste from unused tests; “local COVID-19 testing waste transfer facility” means a waste disposal site, (a) at which COVID-19 testing waste is collected, handled, stored and transferred, and (b) at which no COVID-19 testing waste is treated, processed, deposited or disposed of. O. Reg. 384/21, s. 1. (2) The following provisions do not apply in respect of subject waste that is COVID-19 testing waste destined for disposal at a waste disposal site in Ontario: 1. Sections 17.2, 18, 19 and 21 to 23. 2. Subsections 27 (3) to (7). O. Reg. 384/21, s. 1. (3) Section 16 does not apply in respect of a waste management system if, (a) the only waste management done by the system in respect of COVID-19 testing waste is the collection, handling, transportation, storage or transfer of the waste; and (b) the COVID-19 testing waste is destined for disposal at a waste disposal site in Ontario. O. Reg. 384/21, s. 1. (4) Subsection 27 (1) of the Act does not apply in respect of a waste management system or a waste disposal site if, (a) the only waste management done by the system or at the site in respect of COVID-19 testing waste is the collection, handling, transportation, storage or transfer of the waste; and (b) the COVID-19 testing waste is destined for disposal at a waste disposal site in Ontario. O. Reg. 384/21, s. 1. (5) Section 40 of the Act does not apply in respect of the deposit of, or causing, permitting or arranging for the deposit of, COVID-19 testing waste at a local COVID-19 testing waste transfer facility if the COVID-19 testing waste is destined for disposal at a waste disposal site in Ontario. O. Reg. 384/21, s. 1. (6) Section 41 of the Act does not apply in respect of the use of, or causing, permitting or arranging for the use of, any facilities or equipment for the storage, handling, collection, transfer or transportation of COVID-19 testing waste destined for disposal at a waste disposal site in Ontario. O. Reg. 384/21, s. 1. Stationary Refrigerant Waste 30. (1) A stationary refrigerant waste collector that collects stationary refrigerant waste shall, (a) recycle it for use in air-conditioning units, heat pumps, refrigerators or freezers; or (b) transport it to, (i) a wholesale dealer in refrigerants, (ii) a stationary refrigerant waste recycler, or (iii) a stationary refrigerant waste disposal site that is subject to an environmental compliance approval to handle stationary refrigerant waste. R.R.O. 1990, Reg. 347, s. 30 (1); O. Reg. 190/94, s. 2 (1); O. Reg. 234/11, s. 29 (1). (2) A wholesale dealer in refrigerants that receives stationary refrigerant waste shall transport it to, (a) a stationary refrigerant waste recycler; or (b) a stationary refrigerant waste disposal site that is subject to an environmental compliance approval to handle stationary refrigerant waste. R.R.O. 1990, Reg. 347, s. 30 (2); O. Reg. 234/11, s. 29 (2). (3) A stationary refrigerant waste recycler that receives stationary refrigerant waste shall recycle it for use in air-conditioning units, heat pumps, refrigerators or freezers. R.R.O. 1990, Reg. 347, s. 30 (3); O. Reg. 190/94, s. 2 (2). 31. (1) A stationary refrigerant waste collector shall keep a written record each time that stationary refrigerant waste is, (a) removed and collected, at the stationary refrigerant waste collector’s ordinary place of business, from equipment in which refrigerant is used; (b) received at the stationary refrigerant waste collector’s ordinary place of business, after being removed and collected at another location from equipment in which refrigerant is used; or (c) transported from or recycled at the stationary refrigerant waste collector’s ordinary place of business. R.R.O. 1990, Reg. 347, s. 31 (1). (2) A wholesale dealer in refrigerants shall keep a written record each time that it receives or transports stationary refrigerant waste. R.R.O. 1990, Reg. 347, s. 31 (2). (3) A stationary refrigerant waste recycler shall keep a written record each time that it receives or recycles stationary refrigerant waste. R.R.O. 1990, Reg. 347, s. 31 (3). (4) A record made under this section shall show, (a) the date the stationary refrigerant waste was collected, received, transported or recycled; (b) the source of the stationary refrigerant waste; (c) the quantity collected, received, transported or recycled; (d) the type of stationary refrigerant waste; and (e) what was done with the stationary refrigerant waste. R.R.O. 1990, Reg. 347, s. 31 (4). (5) A record made under this section may be disposed of after two years. R.R.O. 1990, Reg. 347, s. 31 (5). (6) Revoked: O. Reg. 190/94, s. 3. 32. (1) A stationary refrigerant waste disposal site that is the ordinary place of business of a stationary refrigerant waste collector or that is operated by a wholesale dealer in refrigerants is exempt from section 27 of the Act if, (a) access to stationary refrigerant waste is controlled by gates, fencing, attendants or other security measures; (b) containers in which stationary refrigerant waste is stored are clearly marked as to contents; (c) stationary refrigerant waste is stored in a location and manner that prevents damage or deterioration; (d) stored stationary refrigerant waste is readily accessible for inspection by a provincial officer; (e) there is available, at or near the site, firefighting equipment and spill clean-up and containment equipment appropriate to the quantities and types of stationary refrigerant waste on or likely to be on the site; and (f) written notice is given to the Director within ninety days after the establishment of the site, specifying the location of the site and the quantities and types of stationary refrigerant waste on or likely to be on the site. R.R.O. 1990, Reg. 347, s. 32 (1). (2) A stationary refrigerant waste disposal site is exempt from section 27 of the Act if, (a) stationary refrigerant waste is removed and collected on the site from equipment in which refrigerant is used; and (b) the site is not the ordinary place of business of the stationary refrigerant waste collector. R.R.O. 1990, Reg. 347, s. 32 (2). 33. A stationary refrigerant waste management system is exempt from section 27 of the Act if all stationary refrigerant waste disposal sites used in the system are, (a) exempt from section 27 of the Act; or (b) established and operated in accordance with an environmental compliance approval. R.R.O. 1990, Reg. 347, s. 33; O. Reg. 234/11, s. 30. 34. Section 18 does not apply in respect of subject waste that is stationary refrigerant waste unless, (a) a stationary refrigerant waste collector transports stationary refrigerant waste directly from the waste generation facility to, (i) a stationary refrigerant waste recycler, or (ii) a stationary refrigerant waste disposal site that is subject to an environmental compliance approval to handle stationary refrigerant waste; or (b) the waste generation facility is operated by a wholesale dealer in refrigerants. R.R.O. 1990, Reg. 347, s. 34; O. Reg. 234/11, s. 31. 35. Section 19 and sections 21 to 27 do not apply in respect of subject waste that is stationary refrigerant waste being managed in accordance with section 30. O. Reg. 461/05, s. 9. Mobile Refrigerant Waste 36. (1) On and after the 1st day of July, 1991, no person shall discharge or permit the discharge of mobile refrigerant waste into the natural environment. R.R.O. 1990, Reg. 347, s. 36 (1). (2) On and after the 1st day of July, 1991, a person who removes mobile refrigerant waste from equipment in which refrigerant is used shall collect the mobile refrigerant waste. R.R.O. 1990, Reg. 347, s. 36 (2). 37. (1) A mobile refrigerant waste collector that collects mobile refrigerant waste shall, (a) recycle it for use in air-conditioning units, heat pumps, refrigerators or freezers; or (b) transport it to, (i) a mobile refrigerant waste recycler, or (ii) a mobile refrigerant waste disposal site that is subject to an environmental compliance approval to handle mobile refrigerant waste. R.R.O. 1990, Reg. 347, s. 37 (1); O. Reg. 190/94, s. 4 (1); O. Reg. 234/11, s. 32. (2) A mobile refrigerant waste recycler that receives mobile refrigerant waste shall recycle it for use in air-conditioning units, heat pumps, refrigerators or freezers. R.R.O. 1990, Reg. 347, s. 37 (2); O. Reg. 190/94, s. 4 (2). 38. (1) A mobile refrigerant waste collector shall keep a written record each time that mobile refrigerant waste is, (a) removed and collected, at the mobile refrigerant waste collector’s ordinary place of business, from equipment in which refrigerant is used; (b) received at the mobile refrigerant waste collector’s ordinary place of business, after being removed and collected at another location from equipment in which refrigerant is used; or (c) transported from or recycled at the mobile refrigerant waste collector’s ordinary place of business. R.R.O. 1990, Reg. 347, s. 38 (1). (2) A mobile refrigerant waste recycler shall keep a written record each time that it receives or recycles mobile refrigerant waste. R.R.O. 1990, Reg. 347, s. 38 (2). (3) A record made under this section shall show, (a) the date the mobile refrigerant waste was collected, transported, received or recycled; (b) the source of the mobile refrigerant waste; (c) the quantity collected, transported, received or recycled; (d) the type of mobile refrigerant waste; and (e) what was done with the mobile refrigerant waste. R.R.O. 1990, Reg. 347, s. 38 (3). (4) A record made under this section may be disposed of after two years. R.R.O. 1990, Reg. 347, s. 38 (4). (5) Revoked: O. Reg. 190/94, s. 5. 39. (1) A mobile refrigerant waste disposal site that is the ordinary place of business of a mobile refrigerant waste collector is exempt from section 27 of the Act if equipment is kept at the site for collecting mobile refrigerant waste removed from equipment in which refrigerant is used. R.R.O. 1990, Reg. 347, s. 39 (1). (2) A mobile refrigerant waste disposal site is exempt from section 27 of the Act if, (a) mobile refrigerant waste is removed and collected on the site from equipment in which refrigerant is used; and (b) the site is not the ordinary place of business of the mobile refrigerant waste collector. R.R.O. 1990, Reg. 347, s. 39 (2). 40. A mobile refrigerant waste management system is exempt from section 27 of the Act if all mobile refrigerant waste disposal sites used in the system are, (a) exempt from section 27 of the Act; or (b) established and operated in accordance with an environmental compliance approval. R.R.O. 1990, Reg. 347, s. 40; O. Reg. 234/11, s. 33. 41. Section 18 does not apply in respect of subject waste that is mobile refrigerant waste. R.R.O. 1990, Reg. 347, s. 41. 42. Section 19 and sections 21 to 27 do not apply in respect of subject waste that is mobile refrigerant waste being managed in accordance with section 37. O. Reg. 461/05, s. 10. Selected Waste Depots 42.1-42.17 Revoked: O. Reg. 298/94, s. 1. 43. In sections 44 to 59, “lubricant” means crankcase oil, gear oil, transmission fluid and hydraulic fluid; “selected waste depot” means a depot where selected waste is accepted, handled and stored. O. Reg. 298/94, s. 1. 44. (1) For the purposes of this section and sections 45 to 59, the products listed in Column A are selected products and the wastes listed in Column B are selected wastes: Column A Column B 1. anti-freeze 1. waste anti-freeze 2. lubricant 2. waste lubricant 3. oil filters 3. waste oil filters O. Reg. 298/94, s. 1. (2) For the purposes of sections 45 to 59, the types of selected product are those listed in Column A of subsection (1) and the types of selected waste are those listed in Column B of subsection (1). O. Reg. 298/94, s. 1. 45. (1) Sections 47 to 59 apply in relation to selected waste depots that have the following characteristics: 1. The depot is at a location at which a business sells goods or services motor vehicles as one of its primary functions. 2. The depot is managed by a person who owns or has the charge, management or control of the business. 3. The depot is set up to accept, handle and store only selected waste of a type that results from a type of selected product regularly sold at the business. O. Reg. 298/94, s. 1. (2) For the purposes of sections 47 to 59, a business and a depot are associated if they have the relationship to each other set out in paragraphs 1, 2 and 3 of subsection (1). O. Reg. 298/94, s. 1. 46. (1) Sections 27, 40 and 41 of the Act do not apply in relation to a selected waste depot that has the characteristics set out in subsection 45 (1). O. Reg. 298/94, s. 1. (2) Sections 18, 19 and 21 to 27 of this Regulation do not apply to require reports or manifests in respect of selected waste stored at or removed from a selected waste depot that has the characteristics set out in subsection 45 (1). O. Reg. 298/94, s. 1. (3) Sections 27 and 41 of the Act and section 16 of this Regulation do not apply to the transportation of selected waste by the generator of the waste to a selected waste depot that has the characteristics set out in subsection 45 (1), unless the generator of the waste is required to submit a report under section 18 of this Regulation in respect of the waste. O. Reg. 298/94, s. 1. 47. (1) Each operator and owner of a selected waste depot shall ensure that no selected waste is accepted at the depot until 15 days after written notice of intent to operate the depot is given to the Chief Fire Official appointed under subsection 1.1.1. of Division C of Ontario Regulation 213/07 (Fire Code) made under the Fire Protection and Prevention Act, 1997 and to the Director responsible for the region in which the depot is located. O. Reg. 298/94, s. 1; O. Reg. 461/05, s. 11; O. Reg. 234/11, s. 34 (1); O. Reg. 86/16, s. 6. (2) The notice of intent to operate a selected waste depot shall include the following information: 1. The address of the depot and the location of the depot at the address. 2. The name under which the business associated with the depot carries on business. 3. The types of selected waste to be accepted at the depot. 4. The size, type and number of storage containers to be used at the depot. O. Reg. 298/94, s. 1. (3) Each operator and owner of a selected waste depot shall notify the Chief Fire Official and the Director responsible for the region in which the depot is located of any change in respect of the information submitted under this section, no later than 15 days before the change occurs. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 34 (2). 48. Each operator and owner of a selected waste depot shall ensure, by means of gates, fencing, locks, guards or otherwise, that only people authorized by an operator or owner have access to selected waste at the depot. O. Reg. 298/94, s. 1. 49. Each operator and owner of a selected waste depot shall ensure that notice of the days and hours during which selected waste will be accepted at the depot is clearly posted at the depot and shall ensure that selected waste is accepted at the depot only during those days and hours. O. Reg. 298/94, s. 1. 50. Each operator and owner of a selected waste depot shall ensure that any selected waste accepted at the depot is deposited forthwith into storage containers at the depot. O. Reg. 298/94, s. 1. 51. (1) Each operator and owner of a selected waste depot shall ensure that each person who accepts, handles, stores or deposits selected waste at the depot is knowledgeable about, (a) legislation, regulations and Ministry guidelines relevant to the operation of the depot; (b) environmental issues related to the selected waste to be handled at the depot; (c) occupational health and safety issues related to the selected waste to be handled at the depot; (d) the use and operation of any equipment likely to be used in the safe operation of the depot; (e) procedures for dealing with emergencies, including fire and explosion, that might arise at the depot in connection with the selected waste to be handled there; and (f) procedures for dealing with spills of selected waste at the depot, including clean-up, disposal and reporting procedures. O. Reg. 298/94, s. 1. (2) Each operator and owner of a selected waste depot shall ensure that each person who accepts, handles, stores or deposits selected waste at the depot is, (a) an employee of the business associated with the depot; (b) an owner of the business associated with the depot or a person who has the charge, management or control of the business associated with the depot; or (c) an employee of a person mentioned in clause (b). O. Reg. 298/94, s. 1. 52. (1) Each operator and owner of a selected waste depot shall take all reasonable steps to ensure that, (a) selected waste is only accepted at the depot if it is of a type that results from the type of selected product regularly sold at the business associated with the depot; (b) no more than five waste oil filters, no more than 25 litres of waste antifreeze and no more than 25 litres of waste lubricant are accepted at the depot from any one person on any one day; and (c) selected waste is not accepted at the depot if it is brought to the depot by or on behalf of a generator required to submit a report under subsection 18 (1) in respect of the waste. O. Reg. 298/94, s. 1. (2) The taking of all reasonable steps for the purposes of subsection (1) includes ensuring that each person who accepts waste at the depot visually inspects waste before accepting it. O. Reg. 298/94, s. 1. 53. Each operator and owner of a selected waste depot shall ensure that each type of selected waste stored at the depot is stored separate from each other type of selected waste, in storage containers and in accordance with the following rules: 1. Each storage container used to store selected waste shall bear a label or other identification that indicates the type of selected waste that it contains. 2. The label or other identification shall include the name and address of the depot. 3. In the case of an underground storage container, the label or other identification may be located on the fill pipe for the container and need not include the name and address of the depot. 4. The information required to be given on a label or other identification shall be set out so that it is clearly visible and legible. 5. Each storage container used to store selected waste shall be stored, handled and maintained so as to prevent leaks or spills of selected waste, damage or deterioration of the container, or any adverse effect. 6. Each storage container used to store selected waste shall be stored in a manner that facilitates the use of fire fighting equipment and spill containment and clean-up equipment throughout the depot and surrounding area. 7. Each storage container used to store selected waste shall be stored in a manner that facilitates inspection of the depot by a provincial officer. O. Reg. 298/94, s. 1. 54. (1) Each operator and owner of a selected waste depot at which selected waste is stored in an above ground container shall ensure that the depot has a secondary containment system capable of containing leaks or spills of selected waste from the above ground container and capable of preventing the leaks or spills from entering municipal sewers, other drainage systems or the natural environment except air. O. Reg. 298/94, s. 1. (2) In the case of a selected waste depot at which selected waste is stored outdoors in an above ground container the base of which rests on the ground, each operator and owner shall also ensure that the secondary containment system is capable of draining leaks or spills away from the outdoor above ground container. O. Reg. 298/94, s. 1. 55. (1) Each operator and owner of a selected waste depot shall ensure that the depot is equipped with fire fighting equipment and spill containment and clean-up equipment appropriate to the quantities and types of waste stored at the depot. O. Reg. 298/94, s. 1. (2) Each operator and owner of a selected waste depot shall ensure that the equipment mentioned in subsection (1) is stored in a way that makes it immediately accessible in the event that it is needed. O. Reg. 298/94, s. 1. 56. (1) Each operator and owner of a selected waste depot shall ensure that the depot is visually inspected for leaks or spills of selected waste at least once during each day on which the business associated with the depot is open for sales or service. O. Reg. 298/94, s. 1. (2) Each operator and owner of a selected waste depot shall ensure that each inspection performed under subsection (1) on a day on which the depot is open to accept waste is performed by a person knowledgeable about the matters set out in clauses 51 (1) (a) to (f). O. Reg. 298/94, s. 1.

(3) Each operator and owner of a selected waste depot shall ensure that at the time of each inspection under subsection (1) the person performing the inspection legibly records his or her name, the date and the findings of the inspection. O. Reg. 298/94, s. 1. (4) Each operator and owner of a selected waste depot shall ensure that each record made at the depot under subsection (1) is kept at the depot during a period of two years after it is made. O. Reg. 298/94, s. 1. 57. (1) Each operator and owner of a selected waste depot shall ensure that each time selected waste is accepted at the depot, the person accepting the waste legibly records his or her name, the date, the name and address of the person who brought the waste to the depot and the type and approximate quantity of the waste. O. Reg. 298/94, s. 1. (2) Each operator and owner of a selected waste depot shall ensure that each record made at the depot under subsection (1) is kept at the depot during a period of two years after it is made. O. Reg. 298/94, s. 1. 58. (1) Each operator and owner of a selected waste depot shall ensure that no selected waste is accepted at the depot unless there is in effect one or more written agreements each of which meets the requirements of subsections (2) and (3) and that together provide for the ongoing removal of all selected waste from the depot. O. Reg. 120/25, s. 8. (2) An agreement under subsection (1) shall be between an operator or owner of the depot and, (a) a person to whom an environmental compliance approval has been issued that authorizes the person to transport one or more classes of waste that include the type or types of selected waste to be removed from the depot by the person under the agreement; or (b) if transporting one or more classes of waste that include the type or types of selected waste to be removed from the depot is an activity prescribed by section 2 of Ontario Regulation 119/25 (Registrations under Part II.2 of the Act — Waste Transportation Systems) made under the Act, a person engaging in that activity in respect of which a registration under Part II.2 of the Act is in effect. O. Reg. 120/25, s. 8. (3) An agreement under subsection (1) shall state the following: 1. The name and address of the owner or operator of the depot. 2. The name and address of the person responsible for removing waste and the type of selected waste to be removed by the person. 3. The number of the environmental compliance approval that authorizes the person to transport the type of waste, if applicable. 4. The person’s registration number appearing on the confirmation of registration in respect of the activity, if applicable. 5. The name, address and telephone number of an individual able to answer questions about the implementation of the agreement on behalf of the person responsible for removing the waste. 6. The approximate time intervals at which the person responsible for removing the waste will remove the waste. 7. The expiry date of the agreement. O. Reg. 120/25, s. 8. (4) Each operator and owner of a selected waste depot shall ensure that selected waste is removed from the depot only by a person described in clause (2) (a) or (b) who is a party to an agreement under subsection (1) that authorizes the removal of the waste. O. Reg. 120/25, s. 8. (5) Each operator and owner of a selected waste depot shall ensure that a copy of an agreement under subsection (1) is kept at the depot during the term of the agreement and during a period of two years after the termination or expiry of the agreement. O. Reg. 120/25, s. 8. 59. (1) Each operator and owner of a selected waste depot shall ensure that all selected waste is removed from the depot no later than 90 days after the depot ceases to be open to accept selected waste. O. Reg. 298/94, s. 1. (2) Each operator and owner of a selected waste depot shall ensure that written notice is given to the Chief Fire Official appointed under subsection 1.1.1. of Division C of Ontario Regulation 213/07 (Fire Code) made under the Fire Protection and Prevention Act, 1997 and to the Director responsible for the region in which the depot is located no later than 95 days after the depot ceases to be open to accept selected waste. O. Reg. 298/94, s. 1; O. Reg. 461/05, s. 12; O. Reg. 234/11, s. 36 (1); O. Reg. 86/16, s. 6. (3) The notice under subsection (2) shall include the following information: 1. The address of the depot and the location of the depot at the address. 2. The date on which the depot ceased being open to accept selected waste. 3. A statement that all selected waste has been removed from the depot. O. Reg. 298/94, s. 1. (4) Each operator and owner of a selected waste depot shall ensure that any documents required under sections 56 to 58 to be kept at the depot on the date referred to in paragraph 2 of subsection (3) are available to provincial officers for inspection at an address in Ontario during a period of two years after that date. O. Reg. 298/94, s. 1. (5) Each operator and owner of a selected waste depot shall ensure that the Chief Fire Official and the Director responsible for the region in which the depot is located are given timely written notice of the address referred to in subsection (4). O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 36 (2). 60. In the event of conflict between sections 44 to 59 of this Regulation and Ontario Regulation 388/97 (Fire Code) made under the Fire Protection and Prevention Act, 1997 or Ontario Regulation 213/01 (Fuel Oil) made under the Technical Standards and Safety Act, 2000, Ontario Regulation 388/97 or 213/01 prevails. O. Reg. 461/05, s. 13. Pesticide Container Depots 61. In this section and in sections 62 to 73, “empty pesticide container” means an empty container originally used to hold commercial pesticides; “pesticide” means any organism, substance or thing that is manufactured, represented, sold or used as a means of directly or indirectly controlling, preventing, destroying, mitigating, attracting or repelling any pest or of altering the growth, development or characteristics of any plant life that is not a pest and includes any organism, substance or thing registered under the Pest Control Products Act (Canada). O. Reg. 298/94, s. 1. 62. (1) Sections 64 to 73 apply in relation to pesticide container depots that have the following characteristics: 1. The depot is at the place of business of a retail vendor licensed as such under the Pesticides Act. 2. The depot is managed by a person who owns or has the charge, management or control of the retail vendor business. 3. The depot is set up to accept, handle and store only empty pesticide containers. 4. The depot only accepts and stores empty pesticide containers that have been triple or jet rinsed and that do not exceed 23 litres in size if made of plastic or 20 litres in size if made of metal. O. Reg. 298/94, s. 1. (2) For the purposes of sections 64 to 73, a retail vendor business and a pesticide container depot are associated if they have the relationship to each other set out in paragraphs 1, 2 and 3 of subsection (1). O. Reg. 298/94, s. 1. 63. (1) Sections 27, 40 and 41 of the Act do not apply in relation to a pesticide container depot that has the characteristics set out in subsection 62 (1). O. Reg. 298/94, s. 1. (2) Sections 27 and 41 of the Act and section 16 of this Regulation do not apply to the transportation of empty pesticide containers by the generator of the waste to a pesticide container depot that has the characteristics set out in subsection 62 (1). O. Reg. 298/94, s. 1. 64. (1) Each owner and operator of a pesticide container depot shall ensure that no empty pesticide container is accepted at a pesticide container depot until 15 days after written notice of intent to operate the depot is given to the Director. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 37 (1). (2) The notice of intent to operate a pesticide container depot shall include the following information: 1. The address of the pesticide container depot and the location of the pesticide collection depot at that address. 2. The name under which the retail vendor business associated with the pesticide container depot carries on business. 3. The vendor licence number or operator licence number given under the Pesticides Act. 4. The name of the person who owns or has charge, management or control of the retail vendor business. O. Reg. 298/94, s. 1. (3) Each operator and owner of a pesticide container depot shall notify the Director in writing of any change in respect of the information submitted under this section, no later than 15 days before the change occurs. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 37 (2). 65. Each operator and owner of a pesticide container depot shall ensure, by means of gates, fencing, locks, guards or otherwise, that only people authorized by an operator or owner have access to the empty pesticide containers at the pesticide container depot. O. Reg. 298/94, s. 1. 66. Each operator and owner of a pesticide container depot shall ensure that notice of the days and hours during which empty pesticide containers will be accepted at the depot is clearly posted at the depot and shall ensure that empty pesticide containers are accepted at the depot only during those days and hours. O. Reg. 298/94, s. 1. 67. Each operator and owner of a pesticide container depot shall ensure that any empty pesticide containers accepted at the depot are deposited immediately into a storage area at the pesticide container depot. O. Reg. 298/94, s. 1. 68. (1) Each operator and owner of a pesticide container depot shall ensure that each person who accepts, handles, stores or deposits empty pesticide containers at the depot is knowledgeable about, (a) legislation, regulations and Ministry guidelines relevant to the operation of the depot; (b) environmental issues related to the empty pesticide containers to be handled at the depot; (c) occupational health and safety issues related to the empty pesticide containers to be handled at the depot; (d) the use and operation of any equipment likely to be used in the safe operation of the depot; (e) procedures for dealing with emergencies, including fire and explosion, that might arise at the depot in connection with the empty pesticide containers to be handled there; and (f) procedures for dealing with spills relating to the empty pesticide containers at the depot, including clean-up, disposal and reporting procedures. O. Reg. 298/94, s. 1. (2) Each operator and owner of a pesticide container depot shall ensure that each person who accepts, handles, stores or deposits empty pesticide containers at the depot is, (a) an employee of the business associated with the depot; (b) an owner of the business associated with the depot or a person who has the charge, management or control of the business associated with the depot; or (c) an employee of a person mentioned in clause (b). O. Reg. 298/94, s. 1. 69. Each operator and owner of a pesticide container depot shall take all reasonable steps to ensure that each person who accepts empty pesticide containers at the depot visually inspects the empty pesticide containers before accepting them for handling and storage. O. Reg. 298/94, s. 1. 70. Each operator and owner of a pesticide container depot shall ensure that empty pesticide containers stored at the depot are stored in containers or areas in accordance with the following rules: 1. Each container or area used to store empty pesticide containers shall bear a label or other identification that indicates empty pesticide containers are stored within the container or area. 2. The information on the label or other identification shall be clearly visible and legible. 3. Each container used to store empty pesticide containers shall be stored, handled and maintained so as to prevent damage or deterioration of the containers, or any adverse effect. 4. Each container or area used to store empty pesticide containers shall be covered in such a manner so as to prevent rain water infiltration into or on the empty pesticide containers. 5. Each container used to store empty pesticide containers shall be stored in a manner that facilitates the use of fire fighting equipment and spill containment and clean-up equipment throughout the depot and surrounding area. 6. Each container used to store empty pesticide containers shall be stored in a manner that facilitates inspection of the depot by a provincial officer. 7. Each container or area used to store empty pesticide containers shall have ventilation to the outside atmosphere. O. Reg. 298/94, s. 1. 71. Each operator and owner of a pesticide container depot shall ensure that records are kept of the type and quantity of empty pesticide containers accepted at the pesticide container depot. O. Reg. 298/94, s. 1. 72. (1) Each operator and owner of a pesticide container depot shall ensure that no empty pesticide containers are accepted at the depot unless there is in effect one or more written agreements each of which meets the requirements of subsections (2) and (3) and that together provide for the ongoing removal of all empty pesticide containers from the depot. O. Reg. 120/25, s. 9. (2) An agreement under subsection (1) shall be between an operator or owner of the depot and, (a) a person to whom an environmental compliance approval has been issued that authorizes the person to transport the empty pesticide containers to be removed from the depot; or (b) if transporting empty pesticide containers is an activity prescribed by section 2 of Ontario Regulation 119/25 (Registrations under Part II.2 of the Act — Waste Transportation Systems) made under the Act, a person engaging in that activity in respect of which a registration under Part II.2 of the Act is in effect. O. Reg. 120/25, s. 9. (3) An agreement under subsection (1) shall state the following: 1. The name and address of the owner or operator of the pesticide container depot. 2. The name and address of the person responsible for removing the empty pesticide containers. 3. The number of the environmental compliance approval that authorizes the person to transport the empty pesticide containers, if applicable. 4. The person’s registration number appearing on the confirmation of registration in respect of the activity, if applicable. 5. The name, address and telephone number of an individual able to answer questions about the implementation of the agreement on behalf of the person responsible for removing the empty pesticide containers. 6. The approximate time intervals at which the person responsible for removing the waste will remove the waste. 7. The expiry date of the agreement. O. Reg. 120/25, s. 9. (4) Each operator and owner of a pesticide container depot shall ensure that the empty pesticide containers are removed from the depot only by a person described in clause (2) (a) or (b) who is a party to an agreement under subsection (1) that authorizes the removal of the waste. O. Reg. 120/25, s. 9. (5) Each operator and owner of a pesticide container depot shall ensure that a copy of the agreement is kept at the depot during the term of the agreement and for two years after the termination or expiration of the agreement. O. Reg. 120/25, s. 9. 73. (1) Each operator and owner of a pesticide container depot shall ensure that all empty pesticide containers are removed from the depot no later than 90 days after the depot ceases to operate as a pesticide container depot. O. Reg. 298/94, s. 1. (2) Each operator and owner of a pesticide container depot shall ensure that written notice is given to the Director no later than 95 days after the depot ceases to be open to accept empty pesticide containers. O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 39 (1). (3) The notice under subsection (2) shall include the following information: 1. The address of the depot and the location of the depot at the address. 2. The date on which the depot ceased to operate as a pesticide container depot. 3. A statement that all empty pesticide containers have been removed from the pesticide container depot. O. Reg. 298/94, s. 1. (4) Each operator and owner of a pesticide container depot shall ensure that any documents required under sections 71 and 72 are kept at the depot and are available to provincial officers for inspection at an address in Ontario during a period of two years after the date on which the depot ceased to operate as a pesticide container depot. O. Reg. 298/94, s. 1. (5) Each operator and owner of a pesticide container depot shall ensure that the Director is given timely written notice of the address referred to in subsection (4). O. Reg. 298/94, s. 1; O. Reg. 234/11, s. 39 (2). Land Disposal of Hazardous Waste 74. No person shall dispose of PCB waste by land disposal. O. Reg. 461/05, s. 14. 75. (1) No person shall dispose of hazardous waste that is hazardous industrial waste by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules: 1. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Schedule 1 if the waste is an aqueous waste: i. If Column 5 of Schedule 1 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste, A. the waste must be treated in accordance with Schedule 1 using the treatment methods set out for those treatment codes in Schedule 7, and B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7. ii. If Column 5 of Schedule 1 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of composite samples, the concentration of the regulated constituent in the treated waste is less than that concentration. iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs. 2. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Schedule 1 if the waste is a non-aqueous waste: i. If Column 6 of Schedule 1 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste, A. the waste must be treated in accordance with Schedule 1 using the treatment methods set out for those treatment codes in Schedule 7, and B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7. ii. If Column 6 of Schedule 1 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of grab samples, the concentration of the regulated constituent in the treated waste is less than that concentration. iii. For the purpose of subparagraph ii, if the numerical concentration set out in Column 6 of Schedule 1 is expressed as a TCLP concentration, the concentration in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure. iv. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs. 3. If treatment subcategories are set out for the waste in Schedule 1, paragraphs 1 and 2 apply to the treatment subcategory that most closely describes the waste. O. Reg. 461/05, s. 15. (2) Dilution may not be used to comply with subparagraph 1 ii or 2 ii of subsection (1). O. Reg. 461/05, s. 15. (3) Despite subsection (1), a person may dispose of hazardous waste that is hazardous industrial waste by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1). O. Reg. 461/05, s. 15. (4) Revoked: O. Reg. 297/17, s. 1. 76. (1) No person shall dispose of hazardous waste that is acute hazardous waste chemical by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules: 1. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Part A of Schedule 2 if the waste is an aqueous waste: i. If Column 6 of Part A of Schedule 2 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste, A. the waste must be treated in accordance with Part A of Schedule 2 using the treatment methods set out for those treatment codes in Schedule 7, and B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7. ii. If Column 6 of Part A of Schedule 2 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of composite samples, the concentration of the regulated constituent in the treated waste is less than that concentration. iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs. 2. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Part A of Schedule 2 if the waste is a non-aqueous waste: i. If Column 7 of Part A of Schedule 2 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste, A. the waste must be treated in accordance with Part A of Schedule 2 using the treatment methods set out for those treatment codes in Schedule 7, and B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7. ii. If Column 7 of Part A of Schedule 2 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of grab samples, the concentration of the regulated constituent in the treated waste is less than that concentration. iii. For the purpose of subparagraph ii, if the numerical concentration set out in Column 7 of Part A of Schedule 2 is expressed as a TCLP concentration, the concentration in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure. iv. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs. 3. If treatment subcategories are set out for the waste in Part A of Schedule 2, paragraphs 1 and 2 apply to the treatment subcategory that most closely describes the waste. O. Reg. 461/05, s. 15. (2) Dilution may not be used to comply with subparagraph 1 ii or 2 ii of subsection (1). O. Reg. 461/05, s. 15. (3) Despite subsection (1), a person may dispose of hazardous waste that is acute hazardous waste chemical by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1). O. Reg. 461/05, s. 15. (4) Revoked: O. Reg. 297/17, s. 1. 77. (1) No person shall dispose of hazardous waste that is hazardous waste chemical by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules: 1. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Part B of Schedule 2 if the waste is an aqueous waste: i. If Column 6 of Part B of Schedule 2 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste, A. the waste must be treated in accordance with Part B of Schedule 2 using the treatment methods set out for those treatment codes in Schedule 7, and B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7. ii. If Column 6 of Part B of Schedule 2 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of composite samples, the concentration of the regulated constituent in the treated waste is less than that concentration. iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs. 2. Subject to paragraph 3, the following rules apply in respect of each regulated constituent set out for the waste in Part B of Schedule 2 if the waste is a non-aqueous waste: i. If Column 7 of Part B of Schedule 2 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste, A. the waste must be treated in accordance with Part B of Schedule 2 using the treatment methods set out for those treatment codes in Schedule 7, and B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7. ii. If Column 7 of Part B of Schedule 2 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of grab samples, the concentration of the regulated constituent in the treated waste is less than that concentration. iii. For the purpose of subparagraph ii, if the numerical concentration set out in Column 7 of Part B of Schedule 2 is expressed as a TCLP concentration, the concentration in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure. iv. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs. 3. If treatment subcategories are set out for the waste in Part B of Schedule 2, paragraphs 1 and 2 apply to the treatment subcategory that most closely describes the waste. O. Reg. 461/05, s. 15. (2) Dilution may not be used to comply with subparagraph 1 ii or 2 ii of subsection (1). O. Reg. 461/05, s. 15. (3) Despite subsection (1), a person may dispose of hazardous waste that is hazardous waste chemical by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1). O. Reg. 461/05, s. 15. (4) Revoked: O. Reg. 297/17, s. 1. 78. (1) No person shall dispose of hazardous waste that is severely toxic waste by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules: 1. If the waste is an aqueous waste, the waste must be treated so that, in the treated waste, based on an analysis of composite samples, the concentration of the regulated constituent set out for the waste in Schedule 3 is less than the numerical concentration set out for that regulated constituent in Column 6 of Schedule 3. 2. If the waste is a non-aqueous waste, the waste must be treated so that, in the treated waste, based on an analysis of grab samples, the concentration of the regulated constituent set out for the waste in Schedule 3 is less than the numerical concentration set out for that regulated constituent in Column 7 of Schedule 3. O. Reg. 461/05, s. 16. (2) Dilution may not be used to comply with paragraph 1 or 2 of subsection (1). O. Reg. 461/05, s. 16. (3) Despite subsection (1), a person may dispose of hazardous waste that is severely toxic waste by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1). O. Reg. 461/05, s. 16. 79. (1) No person shall dispose of characteristic waste by land disposal unless, before it is land disposed, the waste is treated in accordance with the following rules: 1. Subject to paragraphs 3 and 4, the following rules apply in respect of each regulated constituent set out for the waste in Schedule 5 if the waste is an aqueous waste: i. If Column 5 of Schedule 5 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste, A. the waste must be treated in accordance with Schedule 5 using the treatment methods set out for those treatment codes in Schedule 7, and B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7. ii. If Column 5 of Schedule 5 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of composite samples, the concentration of the regulated constituent in the treated waste is less than that concentration. iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs. iv. If Column 5 of Schedule 5 contains the words “meet Schedule 6 standards” in respect of a land disposal treatment requirement for the waste and, on or after December 31, 2009, the waste is treated in accordance with that requirement, the waste must also be treated so that, based on an analysis of composite samples, the concentration in the treated waste of each regulated constituent listed in Schedule 6 is less than the concentration set out for that regulated constituent in Column 3 of Schedule 6. 2. Subject to paragraphs 3 and 4, the following rules apply in respect of each regulated constituent set out for the waste in Schedule 5 if the waste is a non-aqueous waste: i. If Column 6 of Schedule 5 sets out one or more treatment codes as the land disposal treatment requirement for that regulated constituent of the waste, A. the waste must be treated in accordance with Schedule 5 using the treatment methods set out for those treatment codes in Schedule 7, and B. the treated waste resulting from each treatment method must meet the treatment standard set out for that method in Schedule 7. ii. If Column 6 of Schedule 5 sets out a numerical concentration as the land disposal treatment requirement for that regulated constituent of the waste, the waste must be treated so that, based on an analysis of grab samples, the concentration of the regulated constituent in the treated waste is less than that concentration. iii. If subparagraphs i and ii both apply, the waste only needs to be treated in accordance with one of those subparagraphs. iv. If Column 6 of Schedule 5 contains the words “meet Schedule 6 standards” in respect of a land disposal treatment requirement for the waste and, on or after December 31, 2009, the waste is treated in accordance with that requirement, the waste must also be treated so that, based on an analysis of grab samples, the concentration in the treated waste of each regulated constituent listed in Schedule 6 is less than the concentration set out for that regulated constituent in Column 4 of Schedule 6. v. For the purpose of subparagraphs ii and iv, if the numerical concentration set out in Column 6 of Schedule 5 or Column 4 of Schedule 6 is expressed as a TCLP concentration, the concentration in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure. 3. If Column 5 or 6 of Schedule 5 contains the words “best efforts to achieve” in respect of a numerical concentration that is set out as the land disposal treatment requirement for that regulated constituent of the waste, it is not necessary for the concentration of the regulated constituent in the treated waste to be less than that concentration, but the person treating the waste must use the person’s best efforts to achieve that standard. 4. If treatment subcategories are set out for the waste in Schedule 5, paragraphs 1 to 3 apply to the treatment subcategory that most closely describes the waste. O. Reg. 461/05, s. 17. (2) Dilution may not be used to comply with subparagraph 1 ii or iv or 2 ii or iv of subsection (1). O. Reg. 461/05, s. 17. (3) Nothing in this section requires further treatment for a regulated constituent of a waste if, (a) treatment that is required for the waste by subsection (1) causes the concentration of the regulated constituent in the treated waste to increase; (b) a numerical concentration is set out as the land disposal treatment requirement for that regulated constituent of the waste in, (i) Column 5 of Schedule 5, if the waste is an aqueous waste, or (ii) Column 6 of Schedule 5, if the waste is a non-aqueous waste; and (c) the concentration of the regulated constituent in the untreated waste was less than the concentration referred to in clause (b). O. Reg. 461/05, s. 17. (4) For the purpose of subsection (3), if the numerical concentration referred to in clause (3) (b) is expressed as a TCLP concentration, the concentration of the regulated constituent in the untreated waste and in the treated waste must be determined using the Toxicity Characteristic Leaching Procedure. O. Reg. 461/05, s. 17. (5) Despite subsection (1), a person may dispose of characteristic waste by land disposal if the waste has been treated in a manner that the Director has approved in writing as equivalent to the treatment referred to in subsection (1). O. Reg. 461/05, s. 17. (6) This section does not apply to a hazardous waste that is a characteristic waste and that is also a listed waste if all of the regulated constituents set out for the waste in Schedule 5 are regulated constituents set out for the waste in Schedule 1, Part A of Schedule 2, Part B of Schedule 2 or Schedule 3. O. Reg. 461/05, s. 17. (7) Revoked: O. Reg. 297/17, s. 1. 80. (1) Sections 75, 77 and 79 do not apply to the land disposal of a sealed container if, (a) a certificate described in subsection (3) is affixed to the container; (b) the container does not appear to be broken or leaking; and (c) the seal does not appear to be broken or tampered with. O. Reg. 461/05, s. 18. (2) A generator who transfers a sealed container containing waste shall affix a certificate described in subsection (3) to the container if, (a) all the waste in the container is hazardous industrial waste, hazardous waste chemical or characteristic waste; (b) the waste in the container was produced at the generator’s waste generation facility; (c) the waste generation facility produces a total of less than 100 kilograms of hazardous industrial waste, hazardous waste chemical and characteristic waste in any month; (d) no waste in the container has been mixed, blended, bulked or in any other way intermingled with any other waste or material; (e) the container and its seal comply with any requirements of the Manual; and (f) the total weight of the container and its contents does not exceed 250 kilograms. O. Reg. 461/05, s. 18. (3) The certificate referred to in clause (1) (a) and subsection (2) must contain the following: 1. The name, address and telephone number of the generator. 2. A statement that, pursuant to subsection (1), sections 75, 77 and 79 do not apply to the land disposal of the sealed container, as long as, i. the container does not appear to be broken or leaking, and ii. the seal does not appear to be broken or tampered with. 3. A description of the contents of the container, including, i. a statement that all the waste in the container is hazardous industrial waste, hazardous waste chemical or characteristic waste, ii. a statement that no waste in the container has been mixed, blended, bulked or in any other way intermingled with any other waste or material, and iii. a statement that the waste in the container was produced at the generator’s waste generation facility. 4. A statement that the waste generation facility produces a total of less than 100 kilograms of hazardous industrial waste, hazardous waste chemical and characteristic waste in any month. 5. A statement that the container and its seal comply with any requirements of the Manual. 6. A statement that the total weight of the container and its contents does not exceed 250 kilograms. O. Reg. 461/05, s. 18. 81. Sections 75 to 79 do not apply to the land disposal of hazardous waste that is composed only of combined quantities of individual wastes described in one or more of clauses (n), (p), (q), (r), (s), (t) and (u) of the definition of “hazardous waste” in subsection 1 (1) if, (a) each of the individual wastes was brought to and accepted by a waste disposal site that accepts that type of waste from the general public, handles and temporarily stores it, but does not process or dispose of it; and (b) each of the individual wastes would be hazardous waste if it were produced by a commercial or industrial generator or if it were produced in a larger quantity. O. Reg. 461/05, s. 18. 82. (1) Despite sections 75 to 79, a person may dispose of listed waste or characteristic waste by land disposal if the waste is soil or a soil mixture and the waste is first treated in accordance with the following rules: 1. If the soil or soil mixture is corrosive waste, ignitable waste or reactive waste, it must be treated so that it ceases to be corrosive waste, ignitable waste or reactive waste, as the case may be. 2. For each regulated constituent listed in Schedule 6 that can reasonably be expected to be present in the soil or soil mixture at a concentration that exceeds 10 times the standard set out for that regulated constituent in Column 4 of that Schedule, the soil or soil mixture must be treated so that, i. the concentration of the regulated constituent after the treatment is not more than 10 per cent of the concentration of the regulated constituent before the treatment, or ii. the concentration of the regulated constituent after the treatment is not more than 10 times the standard set out for the regulated constituent in Column 4 of Schedule 6. 3. For the purpose of subparagraph 2 i, the concentration of the regulated constituent shall be based on, i. the total concentration of the regulated constituent in the soil or soil mixture, measured in milligrams per kilogram, if, A. the regulated constituent is a metal, and the soil or soil mixture is treated using a metals removal technology, B. the regulated constituent is carbon disulfide, cyclohexanone or methanol, and the soil or soil mixture is treated using a metals removal technology, or C. the regulated constituent is not a metal and is not carbon disulfide, cyclohexanone or methanol, or ii. if subparagraph i does not apply, the concentration of the regulated constituent in leachate from the treated media, measured in milligrams per litre, when the soil or soil mixture is tested using the Toxicity Characteristic Leaching Procedure. 4. If soil or a soil mixture is treated in accordance with paragraphs 1 to 3 and the residuals from the treatment are characteristic waste that is soil or a soil mixture, paragraphs 1 to 3 also apply to those residuals. O. Reg. 461/05, s. 19. (2) If soil or a soil mixture is treated in accordance with paragraphs 1 to 3 of subsection (1) and the residuals from the treatment are characteristic waste that is not soil or a soil mixture, section 79 applies to those residuals. O. Reg. 461/05, s. 19. 83. (1) In this section, “debris” means solid waste that has a particle size of more than 60 millimetres, and includes material that remains with debris when simple mechanical means or simple physical means are used to separate material that is debris from material that is not debris; “debris mixture” means a mixture of debris and other material where, based on visual inspection, the volume of the mixture is made up primarily of debris. O. Reg. 461/05, s. 19. (2) Despite sections 75 to 79, a person may dispose of a listed waste or a characteristic waste by land disposal if the waste is debris or a debris mixture and the waste is first treated in accordance with the following rules: 1. One or more of the treatment methods listed in Schedule 8 must be used. 2. If Schedule 8 sets out restrictions applicable to a treatment method, that method may be used only in accordance with those restrictions. 3. When a treatment method listed in Schedule 8 is used, the treatment must achieve the standard set out for that treatment method in that Schedule. 4. If more than one treatment method listed in Schedule 8 is used and one of the treatment methods uses an immobilization technology, the method that uses the immobilization technology must be the last treatment method to be used. 5. After the waste is treated, the residuals from the treatment must be separated by simple mechanical means or simple physical means into, i. residuals that are debris, and ii. residuals that are not debris. 6. After the waste is treated, the residuals from the treatment that are debris must not be, i. corrosive waste, ii. ignitable waste, iii. leachate toxic waste, or iv. reactive waste. 7. If waste that is reactive waste because of the presence of cyanide is treated, the residuals from the treatment that are debris must be treated so that they may be land disposed in accordance with section 79 and, for that purpose, the residuals shall be deemed to be waste that is reactive waste because of the presence of cyanide. 8. If waste is treated by spalling, layers of the waste that are removed by spalling must be treated in accordance with the rules set out in this subsection and, for that purpose, the removed layers shall be deemed to be debris. 9. After the waste is treated, residuals from the treatment that are not debris must be treated in accordance with the following rules: i. Residuals that are hazardous waste and are hazardous industrial waste must be treated so that they may be land disposed in accordance with section 75. ii. Residuals that are hazardous waste and are acute hazardous waste chemical must be treated so that they may be land disposed in accordance with section 76. iii. Residuals that are hazardous waste and are hazardous waste chemical must be treated so that they may be land disposed in accordance with section 77. iv. Residuals that are hazardous waste and are severely toxic waste chemical must be treated so that they may be land disposed in accordance with section 78. v. Residuals that are hazardous waste and are leachate toxic waste must be treated so that they may be land disposed in accordance with section 79. vi. Residuals that are hazardous waste and are corrosive waste, ignitable waste or reactive waste must be treated so that they are no longer corrosive waste, ignitable waste or reactive waste, unless subparagraph vii applies. vii. The following residuals from the treatment must be treated so that they may be land disposed in accordance with section 79 if they are hazardous waste: A. Residuals that are reactive waste because of the presence of cyanide. B. Residuals that are ignitable waste, are non-aqueous waste and contain 10 per cent total organic carbon or more. O. Reg. 461/05, s. 19. (3) If debris or a debris mixture is treated in accordance with the rules set out in subsection (2) and an immobilization technology described in Schedule 8 was not used, residuals from the treatment that are debris shall be deemed, for the purposes of this Regulation, not to be listed waste. O. Reg. 461/05, s. 19. (4) Subsection (2) does not apply to debris or a debris mixture that includes any of the following: 1. Lead acid batteries, cadmium batteries or radioactive lead solids. 2. Process residuals, including, i. smelter slag, ii. residues from the treatment of wastewater or other waste, iii. sludge and residues from the treatment of sludge, and iv. residues from air pollution control equipment. 3. Intact containers of hazardous waste that are not ruptured and that retain at least 75 per cent of the volume of the original container. O. Reg. 461/05, s. 19. 84. (1) A generator who transfers any of the following waste to a receiving facility shall, before or at the time the waste is received at the receiving facility, give the receiver notice of the current information relating to the waste that is contained in the Generator Registration Report and any subsequent supplementary Generator Registration Report, as the case may be, submitted by the generator under section 18: 1. Characteristic waste or listed waste that, pursuant to section 75, 76, 77, 78 or 79, may not be land disposed. 2. Waste that was characteristic waste but has been treated so that it is no longer characteristic waste, if the waste may not be disposed of by land disposal under subsection 79 (1). O. Reg. 461/05, s. 20; O. Reg. 324/22, s. 16 (1). (2) Either of the following shall be sufficient for the purposes of providing notice under subsection (1): 1. Providing a paper copy of the information referred to in subsection (1). 2. Providing access to an electronic display of the information referred to in subsection (1). O. Reg. 324/22, s. 16 (2). (3) Revoked: O. Reg. 324/22, s. 16 (2). (4) The generator is only required to comply with subsection (1) in respect of, (a) the first transfer to the receiving facility of each type of characteristic waste or listed waste identified in the Generator Registration Report and any subsequent supplementary Generator Registration Report, as the case may be, submitted by the generator under section 18; and (b) the first transfer to the receiving facility of a type of waste referred to in clause (a) following each significant change to information previously given to the receiver under subsection (1), if the change relates to the description or physical or chemical properties of that type of waste. O. Reg. 461/05, s. 20; O. Reg. 324/22, s. 16 (3). (5) The generator shall make a record of its compliance with subsection (1), including the receiver to whom information was given under subsection (1) and the date the information was given. O. Reg. 461/05, s. 20. (6) The generator shall keep every record made under subsection (5) at the waste generation facility for two years. O. Reg. 461/05, s. 20. (7) If waste is transferred by a generator to a receiving facility, the waste was characteristic waste and the waste can be disposed of by land disposal under section 79, (a) the generator shall, before or at the time the waste is received at the receiving facility, give the receiver notice that the waste was characteristic waste and that the waste can be disposed of by land disposal under section 79; and (b) subsections (2) to (6) apply, with necessary modifications, in respect of a notice required by clause (a). O. Reg. 461/05, s. 20; O. Reg. 324/22, s. 16 (4). 85. (1) A generator or operator of a waste disposal site who treats waste in accordance with section 75, 76, 77, 78, 79, 82 or 83 shall develop and follow a written plan that requires regular and detailed chemical and physical testing of representative samples of the waste. O. Reg. 461/05, s. 21. (2) The person who develops the plan shall ensure that, (a) the plan includes requirements to ensure that the testing will provide all information necessary to treat the waste in accordance with section 75, 76, 77, 78, 79, 82 or 83, as the case may be; (b) the plan specifies the frequency with which testing will be conducted. O. Reg. 461/05, s. 21. (3) A person who develops a plan under subsection (1) shall keep a copy of the plan while that subsection applies to the person and for at least two years after that subsection ceases to apply to the person. O. Reg. 461/05, s. 21. (4) A person who is required to keep a copy of a plan under subsection (3) shall keep it at, (a) the waste generation facility, if the person is a generator, or (b) the waste disposal site, if the person is the operator of a waste disposal site. O. Reg. 461/05, s. 21. (5) The person who is required to follow a plan under subsection (1) shall make a record of the result of every test conducted in accordance with the plan. O. Reg. 461/05, s. 21.

(6) A person who makes a record under subsection (5) shall keep the record for at least two years. O. Reg. 461/05, s. 21. Forms 1, 2 Revoked: O. Reg. 501/01, s. 12. Schedule 1 Hazardous Industrial Waste Hazardous Industrial Waste from Non-Specific Sources Hazardous Industrial Waste Regulated Constituents (and Treatment Subcategories1) Land Disposal Treatment Requirements Aqueous Waste Non-aqueous Waste Column 1 Haz. Waste Number2 Column 2 Waste Column 3 Generic Name or other description Column 4 CAS Number3 Column 5 Treatment Code4 or Concentration5 (mg/L) Column 6 Treatment Code4 or Concentration6 (mg/kg, unless otherwise indicated) F001 The following spent halogenated solvents used in degreasing: Tetrachloroethylene, trichloroethylene, methylene chloride, 1,1,1-trichloroethane, carbon tetrachloride and chlorinated fluorocarbons; all spent solvent mixtures/blends used in degreasing containing, before use, a total of ten per cent or more (by volume) of one or more of the above halogenated solvents or those solvents listed in F002, F004 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. Acetone 67-64-1 0.28 160 Benzene 71-43-2 0.14 10 n-Butyl alcohol 71-36-3 5.6 2.6 Carbon disulfide 75-15-0 3.8 NA Carbon tetrachloride 56-23-5 0.057 6.0 Chlorobenzene 108-90-7 0.057 6.0 o-Cresol 95-48-7 0.11 5.6 m-Cresol (difficult to distinguish from p-cresol) 108-39-4 0.77 5.6 p-Cresol (difficult to distinguish from m-cresol) 106-44-5 0.77 5.6 Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations) 1319-77-3 0.88 11.2 Cyclohexanone 108-94-1 0.36 NA o-Dichlorobenzene 95-50-1 0.088 6.0 Ethyl acetate 141-78-6 0.34 33 Ethyl benzene 100-41-4 0.057 10 Ethyl ether 60-29-7 0.12 160 Isobutyl alcohol 78-83-1 5.6 170 Methanol 67-56-1 5.6 NA Methylene chloride 75-9-2 0.089 30 Methyl ethyl ketone 78-93-3 0.28 36 Methyl isobutyl ketone 108-10-1 0.14 33 Nitrobenzene 98-95-3 0.068 14 Pyridine 110-86-1 0.014 16 Tetrachloroethylene 127-18-4 0.056 6.0 Toluene 108-88-3 0.08 10 1,1,1-Trichloroethane 71-55-6 0.054 6.0 1,1,2-Trichloroethane 79-00-5 0.054 6.0 1,1,2-Trichloro-1,2,2-trifluoroethane 76-13-1 0.057 30 Trichloroethylene 79-01-6 0.054 6.0 Trichlorofluoromethane 75-69-4 0.02 30 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 F002 The following spent halogenated solvents: Tetrachloroethylene, methylene chloride, trichloroethylene, 1,1,1-trichloroethane, chlorobenzene, 1,1,2-trichloro-1,2,2- trifluoroethane, ortho-dichlorobenzene, trichlorofluoromethane and 1,1,2-trichloro-ethane; all spent solvent mixtures/blends containing, before use, a total of ten per cent or more (by volume) of one or more of the above halogenated solvents or those listed in F001, F004 or F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. same as F001 F003 The following spent non-halogenated solvents: Xylene, acetone, ethyl acetate, ethyl benzene, ethyl ether, methyl isobutyl ketone, n-butyl alcohol, cyclohexanone and methanol; all spent solvent mixtures/blends containing, before use, only the above spent non-halogenated solvents; and all spent solvent mixtures/blends containing, before use, one or more of the above non-halogenated solvents, and, a total of ten per cent or more (by volume) of one or more of those solvents listed in F001, F002, F004 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. Treatment Subcategory 1 All F003 wastes, except those identified in Subcategory 2: same as F001 Treatment Subcategory 2 F003 solvent wastes, that contain any combination of one or more of the following three solvents as the only listed F001-5 solvents: carbon disulfide, cyclohexanone and/or methanol: Carbon disulfide 75-15-0 3.8 4.8 mg/L TCLP Cyclohexanone 108-94-1 0.36 0.75 mg/L TCLP Methanol 67-56-1 5.6 0.75 mg/L TCLP F004 The following spent non-halogenated solvents: Cresols and cresylic acid, and nitrobenzene; all spent solvent mixtures/blends containing, before use, a total of ten per cent or more (by volume) of one or more of the above non-halogenated solvents or those solvents listed in F001, F002 and F005; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. same as F001 F005 The following spent non-halogenated solvents: Toluene, methyl ethyl ketone, carbon disulfide, isobutanol, pyridine, benzene, 2-ethoxyethanol, and 2-nitropropane; all spent solvent mixtures/blends containing, before use, a total of ten per cent or more (by volume) of one or more of the above non-halogenated solvents or those solvents listed in F001, F002 or F004; and still bottoms from the recovery of these spent solvents and spent solvent mixtures. Treatment Subcategory 1 All F005 wastes, except those identified in Subcategory 2: same as F001 Treatment Subcategory 2 F005 solvent wastes, that contain any combination of one or more of the following three solvents as the only listed F001-5 solvents: carbon disulfide, cyclohexanone and/or methanol: same as F003 Subcategory 2 same as F003 Subcategory 2 same as F003 Subcategory 2 same as F003 Subcategory 2 Treatment Subcategory 3 F005 solvent waste containing 2-Nitropropane as the only listed F001-5 solvents: 2-Nitropropane 79-46-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST Treatment Subcategory 4 F005 solvent waste containing 2-Ethoxyethanol as the only listed F001-5 solvents: 2-Ethoxyethanol 110-80-5 BIODG; or CMBST CMBST F006 Wastewater treatment sludges from electroplating operations except from the following processes: (1) Sulfuric acid anodizing of aluminum; (2) tin plating on carbon steel; (3) zinc plating (segregated basis) on carbon steel; (4) aluminum or zinc-aluminum plating on carbon steel; (5) cleaning/stripping associated with tin, zinc and aluminum plating on carbon steel; and (6) chemical etching and milling of aluminum. Cadmium 7440-43-9 0.69 0.11 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Lead 7439-92-1 0.69 0.75 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP Silver 7440-22-4 NA 0.14 mg/L TCLP F007 Spent cyanide plating bath solutions from electroplating operations. Cadmium 7440-43-9 NA 0.11 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Lead 7439-92-1 0.69 0.75 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP Silver 7440-22-4 NA 0.14 mg/L TCLP F008 Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process. Cadmium 7440-43-9 NA 0.11 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Lead 7439-92-1 0.69 0.75 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP Silver 7440-22-4 NA 0.14 mg/L TCLP F009 Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process. Cadmium 7440-43-9 NA 0.11 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Lead 7439-92-1 0.69 0.75 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP Silver 7440-22-4 NA 0.14 mg/L TCLP F010 Quenching bath residues from oil baths from metal heat treating operations where cyanides are used in the process. Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 NA F011 Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations. Cadmium 7440-43-9 NA 0.11 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Lead 7439-92-1 0.69 0.75 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP Silver 7440-22-4 NA 0.14 mg/L TCLP F012 Quenching waste water treatment sludges from metal heat treating operations where cyanides are used in the process. Cadmium 7440-43-9 NA 0.11 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Lead 7439-92-1 0.69 0.75 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP Silver 7440-22-4 NA 0.14 mg/L TCLP F019 Wastewater treatment sludges from the chemical conversion coating of aluminum except from the following: (1) Zirconium phosphating in aluminum can washing when such phosphating is an exclusive conversion coating process; (2) Wastewater treatment sludges from the manufacturing of motor vehicles at a referenced manufacturing facility7.1 using a zinc phosphating process, if the wastes are not placed outside on the land prior to shipment for disposal at a waste disposal site approved to accept the waste. Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 F020 Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tri- or tetrachlorophenol, or of intermediates used to produce their pesticide derivatives. (This listing does not include wastes from the production of Hexachlorophene from highly purified 2,4,5- trichlorophenol.) HxCDDs (All Hexachlorodibenzo-p-dioxins) NA 0.000063 0.001 Hx CDFs (All Hexachlorodibenzofurans) NA 0.000063 0.001 PeCDDs (All Pentachlorodibenzo-p-dioxins) NA 0.000063 0.001 PeCDFs (All Pentachlorodibenzofurans) NA 0.000035 0.001 Pentachlorophenol 87-86-5 0.089 7.4 TCDDs (All Tetrachlorodibenzo-p-dioxins) NA 0.000063 0.001 TCDFs (All Tetrachlorodibenzofurans) NA 0.000063 0.001 2,4,5-Trichlorophenol 95-95-4 0.18 7.4 2,4,6-Trichlorophenol 88-06-2 0.035 7.4 2,3,4,6-Tetrachlorophenol 58-90-2 0.03 7.4 F021 Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of pentachlorophenol, or of intermediates used to produce its derivatives. Same as F020 F022 Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tetra-, penta-, or hexachlorobenzenes under alkaline conditions. Same as F020 F023 Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials on equipment previously used for the production or manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tri- and tetrachlorophenols. (This listing does not include wastes from equipment used only for the production or use of Hexachlorophene from highly purified 2,4,5-trichlorophenol.) Same as F020 F024 Process wastes, including but not limited to, distillation residues, heavy ends, tars, and reactor cleanout wastes, from the production of certain chlorinated aliphatic hydrocarbons by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. (This listing does not include wastewaters, wastewater treatment sludges, spent catalysts, and wastes listed in Part A or B of Schedule 2.) All F024 wastes NA CMBST8 CMBST8 2-Chloro-1,3-butadiene 126-99-8 0.057 0.28 3-Chloropropylene 107-05-1 0.036 30 1,1-Dichloroethane 75-34-3 0.059 6.0 1,2-Dichloroethane 107-06-2 0.21 6.0 1,2-Dichloropropane 78-87-5 0.85 18 cis-1,3-Dichloropropylene 10061-01-5 0.036 18 trans-1,3-Dichloropropylene 10061-02-6 0.036 18 bis(2-Ethylhexyl)phthalate 117-81-7 0.28 28 Hexachloroethane 67-72-1 0.055 30 Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP F025 Condensed light ends, spent filters and filter aids, and spent desiccant wastes from the production of certain chlorinated aliphatic hydrocarbons, by free radical catalyzed processes. These chlorinated aliphatic hydrocarbons are those having carbon chain lengths ranging from one to and including five, with varying amounts and positions of chlorine substitution. Treatment Subcategory 1 F025 Light Ends: Carbon tetrachloride 56-23-5 0.057 6.0 Chloroform 67-66-3 0.046 6.0 1,2-Dichloroethane 107-06-2 0.21 6.0 1,1-Dichloroethylene 75-35-4 0.025 6.0 Methylene chloride 75-9-2 0.089 30 1,1,2-Trichloroethane 79-00-5 0.054 6.0 Trichloroethylene 79-01-6 0.054 6.0 Vinyl chloride 75-01-4 0.027 6.0 Treatment Subcategory 2 F025 Spent Filters/Aids and Desiccants: Carbon tetrachloride 56-23-5 0.057 6.0 Chloroform 67-66-3 0.046 6.0 Hexachlorobenzene 118-74-1 0.055 10 Hexachlorobutadiene 87-68-3 0.055 5.6 Hexachloroethane 67-72-1 0.055 30 Methylene chloride 75-9-2 0.089 30 1,1,2-Trichloroethane 79-00-5 0.054 6.0 Trichloroethylene 79-01-6 0.054 6.0 Vinyl chloride 75-01-4 0.27 6.0 F026 Wastes (except wastewater and spent carbon from hydrogen chloride purification) from the production of materials on equipment previously used for the manufacturing use (as a reactant, chemical intermediate, or component in a formulating process) of tetra-, penta-, or hexachlorobenzene under alkaline conditions. Same as F020 F027 Discarded unused formulations containing tri-, tetra-, or pentachlorophenol or discarded unused formulations containing compounds derived from these chlorophenols. (This listing does not include formulations containing Hexachlorophene synthesized from prepurified 2,4,5-trichlorophenol as the sole component.) HxCDDs (All Hexachlorodibenzo-p-dioxins) NA 0.000063 0.001 HxCDFs (All Hexachlorodibenzofurans) NA 0.000063 0.001 PeCDDs (All Pentachlorodibenzo-p-dioxins) NA 0.000063 0.001 PeCDFs (All Pentachlorodibenzofurans) NA 0.000035 0.001 Pentachlorophenol 87-86-5 0.089 7.4 TCDDs (All Tetrachlorodibenzo-p-dioxins) NA 0.000063 0.001 TCDFs (All Tetrachlorodibenzofurans) NA 0.000063 0.001 2,4,5-Trichlorophenol 95-95-4 0.18 7.4 2,4,6-Trichlorophenol 88-06-2 0.035 7.4 2,3,4,6-Tetrachlorophenol 58-90-2 0.03 7.4 F028 Residues resulting from the incineration or thermal treatment of soil contaminated with Hazardous Waste Numbers F020, F021, F022, F023, F026 and F027. HxCDDs (All Hexachlorodibenzo-p-dioxins) NA 0.000063 0.001 HxCDFs (All Hexachlorodibenzofurans) NA 0.000063 0.001 PeCDDs (All Pentachlorodibenzo-p-dioxins) NA 0.000063 0.001 PeCDFs (All Pentachlorodibenzofurans) NA 0.000035 0.001 Pentachlorophenol 87-86-5 0.089 7.4 TCDDs (All Tetrachlorodibenzo-p-dioxins) NA 0.000063 0.001 TCDFs (All Tetrachlorodibenzofurans) NA 0.000063 0.001 2,4,5-Trichlorophenol 95-95-4 0.18 7.4 2,4,6-Trichlorophenol 88-06-2 0.035 7.4 2,3,4,6-Tetrachlorophenol 58-90-2 0.03 7.4 F032 Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that currently use or have previously used chlorophenolic formulations (except potentially cross-contaminated wastes that have had the F032 waste code deleted in accordance with s. 261.359 or potentially cross-contaminated wastes that are otherwise currently regulated as hazardous wastes (i.e., F034 or F035), and where the generator does not resume or initiate use of chlorophenolic formulations). This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol. Acenaphthene 83-32-9 0.059 3.4 Anthracene 120-12-7 0.059 3.4 Benz(a)anthracene 56-55-3 0.059 3.4 Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) 205-99-2 0.11 6.8 Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) 207-08-9 0.11 6.8 Benzo(a)pyrene 50-32-8 0.061 3.4 Chrysene 218-01-9 0.059 3.4 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 2,4-Dimethyl phenol 105-67-9 0.036 14 Fluorene 86-73-7 0.059 3.4 Hexachlorodibenzo-p-dioxins NA 0.000063 or CMBST8 0.001 or CMBST8 Hexachlorodibenzofurans NA 0.000063 or CMBST8 0.001 or CMBST8 Indeno (1,2,3-cd) pyrene 193-39-5 0.0055 3.4 Naphthalene 91-20-3 0.059 5.6 Pentachlorodibenzo-p-dioxins NA 0.000063 or CMBST8 0.001 or CMBST8 Pentachlorodibenzofurans NA 0.000035 or CMBST8 0.001 or CMBST8 Pentachlorophenol 87-86-5 0.089 7.4 Phenanthrene 85-01-8 0.059 5.6 Phenol 108-95-2 0.039 6.2 Pyrene 129-00-0 0.067 8.2 Tetrachlorodibenzo-p-dioxins NA 0.000063 or CMBST8 0.001 or CMBST8 Tetrachlorodibenzofurans NA 0.000063 or CMBST8 0.001 or CMBST8 2,3,4,6-Tetrachlorophenol 58-90-2 0.03 7.4 2,4,6-Trichlorophenol 88-06-2 0.035 7.4 Arsenic 7440-38-2 1.4 5.0 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP F034 Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use creosote formulations. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol. Acenaphthene 83-32-9 0.059 3.4 Anthracene 120-12-7 0.059 3.4 Benz(a)anthracene 56-55-3 0.059 3.4 Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) 205-99-2 0.11 6.8 Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) 207-08-9 0.11 6.8 Benzo(a)pyrene 50-32-8 0.061 3.4 Chrysene 218-01-9 0.059 3.4 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 Fluorene 86-73-7 0.059 3.4 Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4 Naphthalene 91-20-3 0.059 5.6 Phenanthrene 85-01-8 0.059 5.6 Pyrene 129-00-0 0.067 8.2 Arsenic 7440-38-2 1.4 5.0 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP F035 Wastewaters (except those that have not come into contact with process contaminants), process residuals, preservative drippage, and spent formulations from wood preserving processes generated at plants that use inorganic preservatives containing arsenic or chromium. This listing does not include K001 bottom sediment sludge from the treatment of wastewater from wood preserving processes that use creosote and/or pentachlorophenol. Arsenic 7440-38-2 1.4 5.0 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP F037 Petroleum refinery primary oil/water/solids separation sludge - Any sludge generated from the gravitational separation of oil/water/solids during the storage or treatment of process wastewaters and oily cooling wastewaters from petroleum refineries. Such sludges include, but are not limited to, those generated in: oil/water/solids separators; tanks and impoundments; ditches and other conveyances; sumps; and stormwater units receiving dry weather flow. Sludge generated in stormwater units that do not receive dry weather flow, sludges generated from non‑contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges generated in aggressive biological treatment units as defined in s. 261.31(b)(2)9 (including sludges generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and K051 wastes are not included in this listing. This listing does include residuals generated from processing or recycling oil-bearing hazardous secondary materials excluded under s.261.4(a)(12)(i)9, if those residuals are to be disposed of. Acenaphthene 83-32-9 0.059 NA Anthracene 120-12-7 0.059 3.4 Benzene 71-43-2 0.14 10 Benz(a)anthracene 56-55-3 0.059 3.4 Benzo(a)pyrene 50-32-8 0.061 3.4 bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28 Chrysene 218-01-9 0.059 3.4 Di-n-butyl phthalate 84-74-2 0.057 28 Ethylbenzene 100-41-4 0.057 10 Fluorene 86-73-7 0.059 NA Naphthalene 91-20-3 0.059 5.6 Phenanthrene 85-01-8 0.059 5.6 Phenol 108-95-2 0.039 6.2 Pyrene 129-00-0 0.067 8.2 Toluene 108-88-3 0.08 10 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Lead 7439-92-1 0.69 NA Nickel 7440-02-0 NA 11 mg/L TCLP F038 Petroleum refinery secondary (emulsified) oil/water/solids separation sludge - Any sludge and/or float generated from the physical and/or chemical separation of oil/ water/solids in process wastewaters and oily cooling wastewaters from petroleum refineries. Such wastes include, but are not limited to, all sludges and floats generated in: induced air flotation (IAF) units, tanks and impoundments, and all sludges generated in DAF units. Sludges generated in stormwater units that do not receive dry weather flow, sludges generated from non-contact once-through cooling waters segregated for treatment from other process or oily cooling waters, sludges and floats generated in aggressive biological treatment units as defined in s. 261.31(b)(2)9 (including sludges and floats generated in one or more additional units after wastewaters have been treated in aggressive biological treatment units) and F037, K048, and K051 wastes are not included in this listing. Benzene 71-43-2 0.14 10 Benzo(a)pyrene 50-32-8 0.061 3.4 bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28 Chrysene 218-01-9 0.059 3.4 Di-n-butyl phthalate 84-74-2 0.057 28 Ethylbenzene 100-41-4 0.057 10 Fluorene 86-73-7 0.059 NA Naphthalene 91-20-3 0.059 5.6 Phenanthrene 85-01-8 0.059 5.6 Phenol 108-95-2 0.039 6.2 Pyrene 129-00-0 0.067 8.2 Toluene 108-88-3 0.08 10 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Lead 7439-92-1 0.69 NA Nickel 7440-02-0 NA 11 mg/L TCLP F039 Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one hazardous waste. (Leachate resulting from the disposal of one or more of the following Hazardous Wastes and no other Hazardous Wastes retains its Hazardous Waste Number(s): F020, F021, F022, F026, F027, and/or F028.) Acenaphthylene 208-96-8 0.059 3.4 Acenaphthene 83-32-9 0.059 3.4 Acetone 67-64-1 0.28 160 Acetonitrile 75-05-8 5.6 NA Acetophenone 96-86-2 0.01 9.7 2-Acetylaminofluorene 53-96-3 0.059 140 Acrolein 107-02-8 0.29 NA Acrylonitrile 107-13-1 0.24 84 Aldrin 309-00-2 0.021 0.066 4-Aminobiphenyl 92-67-1 0.13 NA Aniline 62-53-3 0.81 14 Anthracene 120-12-7 0.059 3.4 Aramite 140-57-8 0.36 NA alpha-BHC 319-84-6 0.00014 0.066 beta-BHC 319-85-7 0.00014 0.066 delta-BHC 319-86-8 0.023 0.066 gamma-BHC 58-89-9 0.0017 0.066 Benzene 71-43-2 0.14 10 Benz(a)anthracene 56-55-3 0.059 3.4 Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) 205-99-2 0.11 6.8 Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) 207-08-9 0.11 6.8 Benzo(g,h,i)perylene 191-24-2 0.0055 1.8 Benzo(a)pyrene 50-32-8 0.061 3.4 Bromodichloromethane 75-27-4 0.35 15 Methyl bromide (Bromomethane) 74-83-9 0.11 15 4-Bromophenyl phenyl ether 101-55-3 0.055 15 n-Butyl alcohol 71-36-3 5.6 2.6 Butyl benzyl phthalate 85-68-7 0.017 28 2-sec-Butyl-4,6-dinitrophenol (Dinoseb) 88-85-7 0.066 2.5 Carbon disulfide 75-15-0 3.8 NA Carbon tetrachloride 56-23-5 0.057 6.0 Chlordane (alpha and gamma isomers) 57-74-9 0.0033 0.26 p-Chloroaniline 106-47-8 0.46 16 Chlorobenzene 108-90-7 0.057 6.0 Chlorobenzilate 510-15-6 0.1 NA 2-Chloro-1,3-butadiene 126-99-8 0.057 NA Chlorodibromomethane 124-48-1 0.057 15 Chloroethane 75-00-3 0.27 6 bis(2-Chloroethoxy)methane 111-91-1 0.036 7.2 bis(2-Chloroethyl)ether 111-44-4 0.033 6.0 Chloroform 67-66-3 0.046 6.0 bis(2-Chloroisopropyl)ether 39638-32-9 0.055 7.2 p-Chloro-m-cresol 59-50-7 0.018 14 Chloromethane (Methyl chloride) 74-87-3 0.19 30 2-Chloronaphthalene 91-58-7 0.055 5.6 2-Chlorophenol 95-57-8 0.044 5.7 3-Chloropropylene 107-05-1 0.036 30 Chrysene 218-01-9 0.059 3.4 o-Cresol 95-48-7 0.11 5.6 m-Cresol (difficult to distinguish from p-cresol) 108-39-4 0.77 5.6 p-Cresol (difficult to distinguish from m-cresol) 106-44-5 0.77 5.6 Cyclohexanone 108-94-1 0.36 NA 1,2-Dibromo-3-chloropropane 96-12-8 0.11 15 Ethylene dibromide (1,2-Dibromoethane) 106-93-4 0.028 15 Dibromomethane 74-95-3 0.11 15 2,4-D (2,4-Dichlorophenoxyacetic acid) 94-75-7 0.72 10 o,p'-DDD 53-19-0 0.023 0.087 p,p'-DDD 72-54-8 0.023 0.087 o,p'-DDE 3424-82-6 0.031 0.087 p,p'-DDE 72-55-9 0.031 0.087 o,p'-DDT 789-02-6 0.0039 0.087 p,p'-DDT 50-29-3 0.0039 0.087 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 Dibenz(a,e)pyrene 192-65-4 0.061 NA m-Dichlorobenzene 541-73-1 0.036 6.0 o-Dichlorobenzene 95-50-1 0.088 6.0 p-Dichlorobenzene 106-46-7 0.09 6.0 Dichlorodifluoromethane 75-71-8 0.23 7.2 1,1-Dichloroethane 75-34-3 0.059 6.0 1,2-Dichloroethane 107-06-2 0.21 6.0 1,1-Dichloroethylene 75-35-4 0.025 6.0 trans-1,2-Dichloroethylene 156-60-5 0.054 30 2,4-Dichlorophenol 120-83-2 0.044 14 2,6-Dichlorophenol 87-65-0 0.044 14 1,2-Dichloropropane 78-87-5 0.85 18 cis-1,3-Dichloropropylene 10061-01-5 0.036 18 trans-1,3-Dichloropropylene 10061-02-6 0.036 18 Dieldrin 60-57-1 0.017 0.13 Diethyl phthalate 84-66-2 0.2 28 2,4-Dimethyl phenol 105-67-9 0.036 14 Dimethyl phthalate 131-11-3 0.047 28 Di-n-butyl phthalate 84-74-2 0.057 28 1,4-Dinitrobenzene 100-25-4 0.32 2.3 4,6-Dinitro-o-cresol 534-52-1 0.28 160 2,4-Dinitrophenol 51-28-5 0.12 160 2,4-Dinitrotoluene 121-14-2 0.32 140 2,6-Dinitrotoluene 606-20-2 0.55 28 Di-n-octyl phthalate 117-84-0 0.017 28 Di-n-propylnitrosamine 621-64-7 0.4 14 1,4-Dioxane 123-91-1 12 170 Diphenylamine (difficult to distinguish from diphenylnitrosamine) 122-39-4 0.92 NA Diphenylnitrosamine (difficult to distinguish from diphenylamine) 86-30-6 0.92 NA 1,2-Diphenylhydrazine 122-66-7 0.087 NA Disulfoton 298-04-4 0.017 6.2 Endosulfan I 939-98-8 0.023 0.066 Endosulfan II 33213-6-5 0.029 0.13 Endosulfan sulfate 1031-07-8 0.029 0.13 Endrin 72-20-8 0.0028 0.13 Endrin aldehyde 7421-93-4 0.025 0.13 Ethyl acetate 141-78-6 0.34 33 Ethyl cyanide (Propanenitrile) 107-12-0 0.24 360 Ethyl benzene 100-41-4 0.057 10 Ethyl ether 60-29-7 0.12 160 bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28 Ethyl methacrylate 97-63-2 0.14 160 Ethylene oxide 75-21-8 0.12 NA Famphur 52-85-7 0.017 15 Fluoranthene 206-44-0 0.068 3.4 Fluorene 86-73-7 0.059 3.4 Heptachlor 76-44-8 0.0012 0.066 Heptachlor epoxide 1024-57-3 0.016 0.066 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin, (1,2,3,4,6,7,8-HpCDD) 35822-46-9 0.000035 0.0025 1,2,3,4,6,7,8-Heptachlorodibenzofuran, (1,2,3,4,6,7,8-HpCDF) 67562-39-4 0.000035 0.0025 1,2,3,4,7,8,9-Heptachlorodibenzofuran, (1,2,3,4,7,8,9-HpCDF) 55673-89-7 0.000035 0.0025 Hexachlorobenzene 118-74-1 0.055 10 Hexachlorobutadiene 87-68-3 0.055 5.6 Hexachlorocyclopentadiene 77-47-4 0.057 2.4 HxCDDs (All Hexachlorodibenzo-p-dioxins) NA 0.000063 0.001 HxCDFs (All Hexachlorodibenzofurans) NA 0.000063 0.001 Hexachloroethane 67-72-1 0.055 30 Hexachloropropylene 1888-71-7 0.035 30 Indeno (1,2,3-cd) pyrene 193-39-5 0.0055 3.4 Iodomethane 74-88-4 0.019 65 Isobutyl alcohol 78-83-1 5.6 170 Isodrin 465-73-6 0.021 0.066 Isosafrole 120-58-1 0.081 2.6 Kepone 143-50-8 0.0011 0.13 Methacrylonitrile 126-98-7 0.24 84 Methanol 67-56-1 5.6 NA Methapyrilene 91-80-5 0.081 1.5 Methoxychlor 72-43-5 0.25 0.18 3-Methylcholanthrene 56-49-5 0.0055 15 4,4'-Methylene bis(2-chloroaniline) 101-14-4 0.5 30 Methylene chloride 75-09-2 0.089 30 Methyl ethyl ketone 78-93-3 0.28 36 Methyl isobutyl ketone 108-10-1 0.14 33 Methyl methacrylate 80-62-6 0.14 160 Methyl methanesulfonate 66-27-3 0.018 NA Methyl parathion 298-00-0 0.014 4.6 Naphthalene 91-20-3 0.059 5.6 2-Naphthylamine 91-59-8 0.52 NA p-Nitroaniline 100-01-6 0.028 28 Nitrobenzene 98-95-3 0.068 14 5-Nitro-o-toluidine 99-55-8 0.32 28 p-Nitrophenol 100-02-7 0.12 29 N-Nitrosodiethylamine 55-18-5 0.4 28 N-Nitrosodimethylamine 62-75-9 0.4 NA N-Nitroso-di-n-butylamine 924-16-3 0.4 17 N-Nitrosomethylethylamine 10595-95-6 0.4 2.3 N-Nitrosomorpholine 59-89-2 0.4 2.3 N-Nitrosopiperidine 100-75-4 0.013 35 N-Nitrosopyrrolidine 930-55-2 0.013 35 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin, (OCDD) 3268-87-9 0.000063 0.005 1,2,3,4,6,7,8,9-Octachlorodibenzofuran, (OCDF) 39001-02-0 0.000063 0.005 Parathion 56-38-2 0.014 4.6 Total PCBs (sum of all PCB isomers, or all Aroclors) 1336-36-3 0.1 10 Pentachlorobenzene 608-93-5 0.055 10 PeCDDs (All Pentachlorodibenzo-p-dioxins) NA 0.000063 0.001 PeCDFs (All Pentachlorodibenzofurans) NA 0.000035 0.001 Pentachloronitrobenzene 82-68-8 0.055 4.8 Pentachlorophenol 87-86-5 0.089 7.4 Phenacetin 62-44-2 0.081 16 Phenanthrene 85-01-8 0.059 5.6 Phenol 108-95-2 0.039 6.2 Phorate 298-02-2 0.021 4.6 Phthalic anhydride 85-44-9 0.055 NA Pronamide 23950-58-5 0.093 1.5 Pyrene 129-00-0 0.067 8.2 Pyridine 110-86-1 0.014 16 Safrole 94-59-7 0.081 22 Silvex (2,4,5-TP) 93-72-1 0.72 7.9 2,4,5-T 93-76-5 0.72 7.9 1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14 TCDDs (All Tetrachlorodibenzo-p-dioxins) NA 0.000063 0.001 TCDFs (All Tetrachlorodibenzofurans) NA 0.000063 0.001 1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0 1,1,2,2-Tetrachloroethane 79-34-6 0.057 6.0 Tetrachloroethylene 127-18-4 0.056 6.0 2,3,4,6-Tetrachlorophenol 58-90-2 0.03 7.4 Toluene 108-88-3 0.08 10 Toxaphene 8001-35-2 0.0095 2.6 Bromoform (Tribromomethane) 75-25-2 0.63 15 1,2,4-Trichlorobenzene 120-82-1 0.055 19 1,1,1-Trichloroethane 71-55-6 0.054 6.0 1,1,2-Trichloroethane 79-00-5 0.054 6.0 Trichloroethylene 79-01-6 0.054 6.0 Trichlorofluoromethane 75-69-4 0.02 30 2,4,5-Trichlorophenol 95-95-4 0.18 7.4 2,4,6-Trichlorophenol 88-06-2 0.035 7.4 1,2,3-Trichloropropane 96-18-4 0.85 30 1,1,2-Trichloro-1,2,2-trifluoroethane 76-13-1 0.057 30 Tris(2,3-Dibromopropyl) phosphate 126-72-7 0.11 NA Vinyl chloride 75-01-4 0.27 6.0 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 Antimony 7440-36-0 1.9 1.15 mg/L TCLP Arsenic 7440-38-2 1.4 5.0 mg/L TCLP Barium 7440-39-3 1.2 21 mg/L TCLP Beryllium 7440-41-7 0.82 NA Cadmium 7440-43-9 0.69 0.11 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 NA Fluoride 16984-48-8 35 NA Lead 7439-92-1 0.69 0.75 mg/L TCLP Mercury 7439-97-6 0.15 0.25 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP Selenium 7782-49-2 0.82 5.7 mg/L TCLP Silver 7440-22-4 0.43 0.14 mg/L TCLP Sulfide 8496-25-8 14 NA Thallium 7440-28-0 1.4 NA Vanadium 7440-62-2 4.3 NA Hazardous Industrial Waste from Specific Sources Hazardous Industrial Waste Regulated Constituents (and Treatment Subcategories1) Land Disposal Treatment Requirements Aqueous Waste Non-aqueous Waste Column 1 Column 2 Column 3 Column 4 Column 5 Column 6 Haz. Waste Number2 Waste Generic Name or other description CAS Number3 Treatment Code4 or Concentration5 (mg/L) Treatment Code4 or Concentration6 (mg/kg, unless otherwise indicated) Wood preservation: K001 Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote and/or pentachlorophenol. Naphthalene 91-20-3 0.059 5.6 Pentachlorophenol 87-86-5 0.089 7.4 Phenanthrene 85-01-8 0.059 5.6 Pyrene 129-00-0 0.067 8.2 Toluene 108-88-3 0.08 10 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 Lead 7439-92-1 0.69 0.75 mg/L TCLP Inorganic Pigments: K002 Wastewater treatment sludge from the production of chrome yellow and orange pigments. Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP K003 Wastewater treatment sludge from the production of molybdate orange pigments. Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP K004 Wastewater treatment sludge from the production of zinc yellow pigments. Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP K005 Wastewater treatment sludge from the production of chrome green pigments. Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 K006 Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous and hydrated). Treatment Subcategory 1 Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous): Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP Treatment Subcategory 2 Wastewater treatment sludge from the production of chrome oxide green pigments (hydrated): Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 NA K007 Wastewater treatment sludge from the production of iron blue pigments. Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 K008 Oven residue from the production of chrome oxide green pigments. Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP Organic chemicals: K009 Distillation bottoms from the production of acetaldehyde from ethylene. Chloroform 67-66-3 0.046 6.0 K010 Distillation side cuts from the production of acetaldehyde from ethylene. Chloroform 67-66-3 0.046 6.0 K011 Bottom stream from the wastewater stripper in the production of acrylonitrile. Acetonitrile 75-05-8 5.6 38 Acrylonitrile 107-13-1 0.24 84 Acrylamide 79-06-1 19 23 Benzene 71-43-2 0.14 10 Cyanides (Total)7 57-12-5 1.2 590 K013 Bottom stream from the acetonitrile column in the production of acrylonitrile. Acetonitrile 75-05-8 5.6 38 Acrylonitrile 107-13-1 0.24 84 Acrylamide 79-06-1 19 23 Benzene 71-43-2 0.14 10 Cyanides (Total)7 57-12-5 1.2 590 K014 Bottoms from the acetonitrile purification column in the production of acrylonitrile. Acetonitrile 75-05-8 5.6 38 Acrylonitrile 107-13-1 0.24 84 Acrylamide 79-06-1 19 23 Benzene 71-43-2 0.14 10 Cyanides (Total)7 57-12-5 1.2 590 K015 Still bottoms from the distillation of benzyl chloride. Anthracene 120-12-7 0.059 3.4 Benzal chloride 98-87-3 0.055 6.0 Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) 205-99-2 0.11 6.8 Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) 207-08-9 0.11 6.8 Phenanthrene 85-01-8 0.059 5.6 Toluene 108-88-3 0.08 10 Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP K016 Heavy ends or distillation residues from the production of carbon tetrachloride. Hexachlorobenzene 118-74-1 0.055 10 Hexachlorobutadiene 87-68-3 0.055 5.6 Hexachlorocyclopentadiene 77-47-4 0.057 2.4 Hexachloroethane 67-72-1 0.055 30 Tetrachloroethylene 127-18-4 0.056 6.0 K017 Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin. bis(2-Chloroethyl)ether 111-44-4 0.033 6.0 1,2-Dichloropropane 78-87-5 0.85 18 1,2,3-Trichloropropane 96-18-4 0.85 30 K018 Heavy ends from the fractionation column in ethyl chloride production. Chloroethane 75-00-3 0.27 6.0 Chloromethane 74-87-3 0.19 NA 1,1-Dichloroethane 75-34-3 0.059 6.0 1,2-Dichloroethane 107-06-2 0.21 6.0 Hexachlorobenzene 118-74-1 0.055 10 Hexachlorobutadiene 87-68-3 0.055 5.6 Hexachloroethane 67-72-1 0.055 30 Pentachloroethane 76-01-7 NA 6.0 1,1,1-Trichloroethane 71-55-6 0.054 6.0 K019 Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production. bis(2-Chloroethyl)ether 111-44-4 0.033 6.0 Chlorobenzene 108-90-7 0.057 6.0 Chloroform 67-66-3 0.046 6.0 p-Dichlorobenzene 106-46-7 0.09 NA 1,2-Dichloroethane 107-06-2 0.21 6.0 Fluorene 86-73-7 0.059 NA Hexachloroethane 67-72-1 0.055 30 Naphthalene 91-20-3 0.059 5.6 Phenanthrene 85-01-8 0.059 5.6 1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 NA Tetrachloroethylene 127-18-4 0.056 6.0 1,2,4-Trichlorobenzene 120-82-1 0.055 19 1,1,1-Trichloroethane 71-55-6 0.054 6.0 K020 Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production. 1,2-Dichloroethane 107-06-2 0.21 6.0 1,1,2,2-Tetrachloroethane 79-34-6 0.057 6.0 Tetrachloroethylene 127-18-4 0.056 6.0 K021 Aqueous spent antimony catalyst waste from fluoromethanes production. Carbon tetrachloride 56-23-5 0.057 6.0 Chloroform 67-66-3 0.046 6.0 Antimony 7440-36-0 1.9 1.15 mg/L TCLP K022 Distillation bottom tars from the production of phenol/acetone from cumene. Toluene 108-88-3 0.08 10 Acetophenone 96-86-2 0.01 9.7 Diphenylamine (difficult to distinguish from diphenylnitrosamine) 122-39-4 0.92 13 Diphenylnitrosamine (difficult to distinguish from diphenylamine) 86-30-6 0.92 13 Phenol 108-95-2 0.039 6.2 Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP K023 Distillation light ends from the production of phthalic anhydride from naphthalene. Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) 100-21-0; 85-44-9 0.055 28 K024 Distillation bottoms from the production of phthalic anhydride from naphthalene. Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) 100-21-0; 85-44-9 0.055 28 K025 Distillation bottoms from the production of nitrobenzene by the nitration of benzene. Distillation bottoms from the production of nitrobenzene by the nitration of benzene. NA LLEXT fb SSTRP fb CARBN; or CMBST CMBST K026 Stripping still tails from the production of methyl ethyl pyridines. Stripping still tails from the production of methyl ethyl pyridines. NA CMBST CMBST K027 Centrifuge and distillation residues from toluene diisocyanate production. Centrifuge and distillation residues from toluene diisocyanate production. NA CARBN; or CMBST CMBST K028 Spent catalyst from the hydrochlorinator reactor in the productions of 1,1,1trichloroethane. 1,1-Dichloroethane 75-34-3 0.059 6.0 trans-1,2-Dichloroethylene 156-60-5 0.054 30 Hexachlorobutadiene 87-68-3 0.055 5.6 Hexachloroethane 67-72-1 0.055 30 Pentachloroethane 76-01-7 NA 6.0 1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0 1,1,2,2-Tetrachloroethane 79-34-6 0.057 6.0 Tetrachloroethylene 127-18-4 0.056 6.0 1,1,1-Trichloroethane 71-55-6 0.054 6.0 1,1,2-Trichloroethane 79-00-5 0.054 6.0 Cadmium 7440-43-9 0.69 NA Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP K029 Waste from the product stream stripper in the production of 1,1,1trichloroethane. Chloroform 67-66-3 0.046 6.0 1,2-Dichloroethane 107-06-2 0.21 6.0 1,1-Dichloroethylene 75-35-4 0.025 6.0 1,1,1-Trichloroethane 71-55-6 0.054 6.0 Vinyl chloride 75-01-4 0.27 6.0 K030 Column bottoms or heavy ends from the combined production of trichloroethylene and perchloroethylene. o-Dichlorobenzene 95-50-1 0.088 NA p-Dichlorobenzene 106-46-7 0.09 NA Hexachlorobutadiene 87-68-3 0.055 5.6 Hexachloroethane 67-72-1 0.055 30 Hexachloropropylene 1888-71-7 NA 30 Pentachlorobenzene 608-93-5 NA 10 Pentachloroethane 76-01-7 NA 6.0 1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14 Tetrachloroethylene 127-18-4 0.056 6 1,2,4-Trichlorobenzene 120-82-1 0.055 19 K083 Distillation bottoms from aniline production. Aniline 62-53-3 0.81 14 Benzene 71-43-2 0.14 10 Cyclohexanone 108-94-1 0.36 NA Diphenylamine (difficult to distinguish from diphenylnitrosamine) 122-39-4 0.92 13 Diphenylnitrosamine (difficult to distinguish from diphenylamine) 86-30-6 0.92 13 Nitrobenzene 98-95-3 0.068 14 Phenol 108-95-2 0.039 6.2 Nickel 7440-02-0 3.98 11 mg/L TCLP K085 Distillation or fractionation column bottoms from the production of chlorobenzenes. Benzene 71-43-2 0.14 10 Chlorobenzene 108-90-7 0.057 6.0 m-Dichlorobenzene 541-73-1 0.036 6.0 o-Dichlorobenzene 95-50-1 0.088 6.0 p-Dichlorobenzene 106-46-7 0.09 6.0 Hexachlorobenzene 118-74-1 0.055 10 Total PCBs (sum of all PCB isomers, or all Aroclors) 1336-36-3 0.1 10 Pentachlorobenzene 608-93-5 0.055 10 1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14 1,2,4-Trichlorobenzene 120-82-1 0.055 19 K093 Distillation light ends from the production of phthalic anhydride from orthoxylene. Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) 100-21-0; 85-44-9 0.055 28 K094 Distillation bottoms from the production of phthalic anhydride from orthoxylene. Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) 100-21-0; 85-44-9 0.055 28 K095 Distillation bottoms from the production of 1,1,1trichloroethane. Hexachloroethane 67-72-1 0.055 30 Pentachloroethane 76-01-7 0.055 6.0 1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0 1,1,2,2-Tetrachloroethane 79-34-6 0.057 6.0 Tetrachloroethylene 127-18-4 0.056 6.0 1,1,2-Trichloroethane 79-00-5 0.054 6.0 Trichloroethylene 79-01-1 0.054 6.0 K096 Heavy ends from the heavy ends column from the production of 1,1,1trichloroethane. m-Dichlorobenzene 541-73-1 0.036 6.0 Pentachloroethane 76-01-1 0.055 6.0 1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0 1,1,2,2-Tetrachloroethane 79-34-6 0.057 6.0 Tetrachloroethylene 127-18-4 0.056 6.0 1,2,4-Trichlorobenzene 120-82-1 0.055 19 1,1,2-Trichloroethane 79-00-5 0.054 6.0 Trichloroethylene 79-01-6 0.054 6.0 K103 Process residues from aniline extraction from the production of aniline. Aniline 62-53-3 0.81 14 Benzene 71-43-2 0.14 10 2,4-Dinitrophenol 51-28-5 0.12 160 Nitrobenzene 98-95-3 0.068 14 Phenol 108-95-2 0.039 6.2 K104 Combined wastewater streams generated from nitrobenzene/aniline production. Aniline 62-53-3 0.81 14 Benzene 71-43-2 0.14 10 2,4-Dinitrophenol 51-28-5 0.12 160 Nitrobenzene 98-95-3 0.068 14 Phenol 108-95-2 0.039 6.2 Cyanides (Total)7 57-12-5 1.2 590 K105 Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes. Benzene 71-43-2 0.14 10 Chlorobenzene 108-90-7 0.057 6.0 2-Chlorophenol 95-57-8 0.044 5.7 o-Dichlorobenzene 95-50-1 0.088 6.0 p-Dichlorobenzene 106-46-7 0.09 6.0 Phenol 108-95-2 0.039 6.2 2,4,5-Trichlorophenol 95-95-4 0.18 7.4 2,4,6-Trichlorophenol 88-06-2 0.035 7.4 K107 Column bottoms from product separation from the production of 1,1-dimethyl-hydra-zine (UDMH) from carboxylic acid hydrazines. Column bottoms from product separation from the production of 1,1-dimethyl-hydra-zine (UDMH) from carboxylic acid hydrazines. NA CMBST; or CHOXD fb CARBN; or BIODG fb CARBN CMBST K108 Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. NA CMBST; or CHOXD fb CARBN; or BIODG fb CARBN CMBST K109 Spent filter cartridges from product purification from the production of 1,1- dimethylhydrazine (UDMH) from carboxylic acid hydrazides. Spent filter cartridges from product purification from the production of 1,1- dimethylhydrazine (UDMH) from carboxylic acid hydrazides. NA CMBST; or CHOXD fb CARBN; or BIODG fb CARBN CMBST K110 Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides. NA CMBST; or CHOXD fb CARBN; or BIODG fb CARBN CMBST K111 Product washwaters from the production of dinitrotoluene via nitration of toluene. 2,4-Dinitrotoluene 121-1-2 0.32 140 2,6-Dinitrotoluene 606-20-2 0.55 28 K112 Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene. Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene. NA CMBST; or CHOXD fb CARBN; or BIODG fb CARBN CMBST K113 Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. NA CARBN; or CMBST CMBST K114 Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. NA CARBN; or CMBST CMBST K115 Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. Nickel 7440-02-0 3.98 11 mg/L TCLP Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene. NA CARBN; or CMBST CMBST K116 Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine. Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine. NA CARBN; or CMBST CMBST K117 Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene. Methyl bromide (Bromomethane) 74-83-9 0.11 15 Chloroform 67-66-3 0.046 6.0 Ethylene dibromide (1,2-Dibromoethane) 106-93-4 0.028 15 K118 Spent adsorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene. Methyl bromide (Bromomethane) 74-83-9 0.11 15 Chloroform 67-66-3 0.046 6.0 Ethylene dibromide (1,2-Dibromoethane) 106-93-4 0.028 15 K136 Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene. Methyl bromide (Bromomethane) 74-83-9 0.11 15 Chloroform 67-66-3 0.46 6.0 Ethylene dibromide (1,2-Dibromoethane) 106-93-4 0.028 15 K149 Distillation bottoms from the production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. (This waste does not include still bottoms from the distillation of benzyl chloride.) Chlorobenzene 108-90-7 0.057 6.0 Chloroform 67-66-3 0.046 6.0 Chloromethane 74-87-3 0.19 30 p-Dichlorobenzene 106-46-7 0.09 6.0 Hexachlorobenzene 118-74-1 0.055 10 Pentachlorobenzene 608-93-5 0.055 10 1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14 Toluene 108-88-3 0.08 10 K150 Organic residuals, excluding spent carbon adsorbent, from the spent chlorine gas and hydrochloric acid recovery processes associated with the production of alpha-( or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. Carbon tetrachloride 56-23-5 0.057 6.0 Chloroform 67-66-3 0.046 6.0 Chloromethane 74-87-3 0.019 30 p-Dichlorobenzene 106-46-7 0.09 6.0 Hexachlorobenzene 118-74-1 0.055 10 Pentachlorobenzene 608-93-5 0.055 10 1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14 1,1,2,2-Tetrachloroethane 79-34-5 0.057 6.0 Tetrachloroethylene 127-18-4 0.056 6.0 1,2,4-Trichlorobenzene 120-82-1 0.055 19 K151 Wastewater treatment sludges, excluding neutralization and biological sludges, generated during the treatment of wastewaters from the production of alpha- (or methyl-) chlorinated toluenes, ring-chlorinated toluenes, benzoyl chlorides, and compounds with mixtures of these functional groups. Benzene 71-43-2 0.14 10 Carbon tetrachloride 56-23-5 0.057 6.0 Chloroform 67-66-3 0.046 6.0 Hexachlorobenzene 118-74-1 0.055 10 Pentachlorobenzene 608-93-5 0.055 10 1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14 Tetrachloroethylene 127-18-4 0.056 6.0 Toluene 108-88-3 0.08 10 K156 Organic waste (including heavy ends, still bottoms, light ends, spent solvents, filtrates, and decantates) from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2- propynyl n-butylcarbamate.) Acetonitrile 75-05-8 5.6 1.8 Acetophenone 96-86-2 0.01 9.7 Aniline 62-53-3 0.81 14 Benomyl 17804-35-2 0.056 1.4 Benzene 71-43-2 0.14 10 Carbaryl 63-25-2 0.006 0.14 Carbendazim 10605-21-7 0.056 1.4 Carbofuran 1563-66-2 0.006 0.14 Carbosulfan 55285-14-8 0.028 1.4 Chlorobenzene 108-90-7 0.057 6.0 Chloroform 67-66-3 0.046 6.0 o-Dichlorobenzene 95-50-1 0.088 6.0 Methomyl 16752-77-5 0.028 0.14 Methylene chloride 75-09-2 0.089 30 Methyl ethyl ketone 78-93-3 0.28 36 Naphthalene 91-20-3 0.059 5.6 Phenol 108-95-2 0.039 6.2 Pyridine 110-86-1 0.014 16 Toluene 108-88-3 0.08 10 Triethylamine 101-44-8 0.081 1.5 K157 Wastewaters (including scrubber waters, condenser waters, washwaters, and separation waters) from the production of carbamates and carbamoyl oximes.

(This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.) Carbon tetrachloride 56-23-5 0.057 6.0 Chloroform 67-66-3 0.046 6.0 Chloromethane 74-87-3 0.19 30 Methomyl 16752-77-5 0.028 0.14 Methylene chloride 75-09-2 0.089 30 Methyl ethyl ketone 78-93-3 0.28 36 Pyridine 110-86-1 0.014 16 Triethylamine 121-44-8 0.081 1.5 K158 Bag house dusts and filter/separation solids from the production of carbamates and carbamoyl oximes. (This listing does not apply to wastes generated from the manufacture of 3-iodo-2-propynyl n-butylcarbamate.) Benomyl 17804-35-2 0.056 1.4 Benzene 71-43-2 0.14 10 Carbendazim 10605-21-7 0.056 1.4 Carbofuran 1563-66-2 0.006 0.14 Carbosulfan 55285-14-8 0.028 1.4 Chloroform 67-66-3 0.046 6.0 Methylene chloride 75-09-2 0.089 30 Phenol 108-95-2 0.039 6.2 K159 Organics from the treatment of thiocarbamate wastes. Benzene 71-43-2 0.14 10 Butylate 2008-41-5 0.042 1.4 EPTC (Eptam) 759-94-4 0.042 1.4 Molinate 2212-67-1 0.042 1.4 Pebulate 1114-71-2 0.042 1.4 Vernolate 1929-77-7 0.042 1.4 K161 Purification solids (including filtration, evaporation, and centrifugation solids), bag house dust and floor sweepings from the production of dithiocarbamate acids and their salts. (This listing does not include K125 or K126.) Antimony 7440-36-0 1.9 1.15 mg/L TCLP Arsenic 7440-38-2 1.4 5.0 mg/L TCLP Carbon disulfide 75-15-0 3.8 4.8 mg/L TCLP Dithiocarbamates (total) NA 0.028 28 Lead 7439-92-1 0.69 0.75 mg/L TCLP Nickel 7440-02-0 3.98 11.0 mg/L TCLP Selenium 7782-49-2 0.82 5.7 mg/L TCLP K174 Wastewater treatment sludges from the production of ethylene dichloride or vinyl chloride monomer. 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin, (1,2,3,4,6,7,8-HpCDD) 35822-46-9 0.000035 or CMBST8 0.0025 or CMBST8 1,2,3,4,6,7,8-Heptachlorodibenzofuran, (1,2,3,4,6,7,8-HpCDF) 67562-39-4 0.000035 or CMBST8 0.0025 or CMBST8 1,2,3,4,7,8,9-Heptachlorodibenzofuran, (1,2,3,4,7,8,9-HpCDF) 55673-89-7 0.000035 or CMBST8 0.0025 or CMBST8 HxCDDs (All Hexachlorodibenzo-p-dioxins) 34465-46-8 0.000063 or CMBST8 0.001 or CMBST8 HxCDFs (All Hexachlorodibenzofurans) 55684-94-1 0.000063 or CMBST8 0.001 or CMBST8 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin, (OCDD) 3268-87-9 0.000063 or CMBST8 0.005 or CMBST8 1,2,3,4,6,7,8,9-Octachlorodibenzofuran, (OCDF) 39001-02-0 0.000063 or CMBST8 0.005 or CMBST8 PeCDDs (All Pentachlorodibenzo-p-dioxins 36088-22-9 0.000063 or CMBST8 0.001 or CMBST8 PeCDFs (All Pentachlorodibenzofurans) 30402-15-4 0.000035 or CMBST8 0.001 or CMBST8 TCDDs (All tetachlorodibenzo-p-dioxins) 41903-57-5 0.000063 or CMBST8 0.001 or CMBST8 TCDFs (All tetrachlorodibenzofurans) 55722-27-5 0.000063 or CMBST8 0.001 or CMBST8 Arsenic 7440-36-0 1.4 5.0 mg/L TCLP K175 Wastewater treatment sludge from the production of vinyl chloride monomer using mercuric chloride catalyst in an acetylene-based process. Mercury 7439-97-6 0.15 0.025 mg/L TCLP10 pH NA pH≤ 6.010 Inorganic chemicals: K071 Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used. Treatment Subcategory 1 Non-aqueous wastes that are residues from RMERC: Mercury 7439-97-6 NA 0.20 mg/L TCLP Treatment Subcategory 2 Non-aqueous wastes that are not residues from RMERC: Mercury 7439-97-6 NA 0.025 mg/L TCLP Treatment Subcategory 3 All K071 aqueous wastes: Mercury 7439-97-6 0.15 NA K073 Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production. Carbon tetrachloride 56-23-5 0.057 6.0 Chloroform 67-66-3 0.046 6.0 Hexachloroethane 67-72-1 0.055 30 Tetrachloroethylene 127-18-4 0.056 6.0 1,1,1-Trichloroethane 71-55-6 0.054 6.0 K106 Wastewater treatment sludge from the mercury cell process in chlorine production. Treatment Subcategory 1 Non-aqueous wastes that contain greater than or equal to 260 mg/kg total mercury: Mercury 7439-97-6 NA RMERC Treatment Subcategory 2 Non-aqueous wastes that contain less than 260 mg/kg total mercury that are residues from RMERC: Mercury 7439-97-6 NA 0.20 mg/L TCLP Treatment Subcategory 3 Other K106 non-aqueous wastes that contain less than 260 mg/kg total mercury and are not residues from RMERC: Mercury 7439-97-6 NA 0.025 mg/L TCLP Treatment Subcategory 4 All K106 aqueous wastes: Mercury 7439-97-6 0.15 NA K176 Baghouse filters from the production of antimony oxide, including filters from the production of intermediates (e.g., antimony metal or crude antimony oxide). Antimony 7440-36-0 1.9 1.15 mg/L TCLP Arsenic 7440-38-2 1.4 5.0 mg/L TCLP Cadmium 7440-43-9 0.69 0.11 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP Mercury 7439-97-6 0.15 0.025 mg/L TCLP K177 Slag from the production of antimony oxide that is speculatively accumulated or disposed, including slag from the production of intermediates (e.g., antimony metal or crude antimony oxide). Antimony 7440-36-0 1.9 1.15 mg/L TCLP Arsenic 7440-38-2 1.4 5.0 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP K178 Residues from manufacturing and manufacturing-site storage of ferric chloride from acids formed during the production of titanium dioxide using the chloride-ilmenite process. 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin, (1,2,3,4,6,7,8-HpCDD) 35822-46-9 0.000035 or CMBST8 0.0025 or CMBST8 1,2,3,4,6,7,8-Heptachlorodibenzofuran, (1,2,3,4,6,7,8-HpCDF) 67562-39-4 0.000035 or CMBST8 0.0025 or CMBST8 1,2,3,4,7,8,9-Heptachlorodibenzofuran, (1,2,3,4,7,8,9-HpCDF) 55673-89-7 0.000035 or CMBST8 0.0025 or CMBST8 HxCDDs (All Hexachlorodibenzo-p-dioxins) 34465-46-8 0.000063 or CMBST8 0.001 or CMBST8 HxCDFs (All Hexachlorodibenzofurans) 55684-94-1 0.000063 or CMBST8 0.001 or CMBST8 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin, (OCDD) 3268-87-9 0.000063 or CMBST8 0.005 or CMBST8 1,2,3,4,6,7,8,9-Octachlorodibenzofuran, (OCDF) 39001-02-0 0.000063 or CMBST8 0.005 or CMBST8 PeCDDs (All Pentachlorodibenzo-p-dioxins 36088-22-9 0.000063 or CMBST8 0.001 or CMBST8 PeCDFs (All Pentachlorodibenzofurans) 30402-15-4 0.000035 or CMBST8 0.001 or CMBST8 TCDDs (All tetachlorodibenzo-p-dioxins) 41903-57-5 0.000063 or CMBST8 0.001 or CMBST8 TCDFs (All tetrachlorodibenzofurans) 55722-27-5 0.000063 or CMBST8 0.001 or CMBST8 Thallium 7440-28-0 1.4 0.20 mg/L TCLP Pesticides: K031 Byproduct salts generated in the production of MSMA and cacodylic acid. Arsenic 7440-38-2 14 5.0 mg/L TCLP K032 Wastewater treatment sludge from the production of chlordane. Hexachlorocyclopentadiene 77-47-4 0.057 2.4 Chlordane (alpha and gamma isomers) 57-74-9 0.0033 0.26 Heptachlor 76-44-8 0.0012 0.066 Heptachlor epoxide 1024-57-3 0.016 0.066 K033 Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane. Hexachlorocyclopentadiene 77-47-4 0.057 2.4 K034 Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane. Hexachlorocyclopentadiene 77-47-4 0.057 2.4 K035 Wastewater treatment sludges generated in the production of creosote. Acenaphthene 83-32-9 NA 3.4 Anthracene 120-12-7 NA 3.4 Benz(a)anthracene 56-55-3 0.059 3.4 Benzo(a)pyrene 50-32-8 0.061 3.4 Chrysene 218-01-9 0.059 3.4 o-Cresol 95-48-7 0.11 5.6 m-Cresol (difficult to distinguish from p-cresol) 108-39-4 0.77 5.6 p-Cresol (difficult to distinguish from m-cresol) 106-44-5 0.77 5.6 Dibenz(a,h)anthracene 53-70-3 NA 8.2 Fluoranthene 206-44-0 0.068 3.4 Fluorene 86-73-7 NA 3.4 Indeno(1,2,3-cd)pyrene 193-39-5 NA 3.4 Naphthalene 91-20-3 0.059 5.6 Phenanthrene 85-01-1 0.059 5.6 Phenol 108-95-2 0.039 6.2 Pyrene 129-00-0 0.067 8.2 K036 Still bottoms from toluene reclamation distillation in the production of disulphoton. Disulfoton 298-04-4 0.017 6.2 K037 Wastewater treatment sludges from the production of disulphoton. Disulfoton 298-04-4 0.017 6.2 Toluene 108-88-3 0.08 10 K038 Wastewater from the washing and stripping of phorate production. Phorate 298-02-2 0.021 4.6 K039 Filter cake from the filtration of diethyl phosphorodithioic acid in the production of phorate. Filter cake from the filtration of diethyl phosphorodithioic acid in the production of phorate. NA CARBN; or CMBST CMBST K040 Wastewater treatment sludge from the production of phorate. Phorate 298-02-2 0.021 4.6 K041 Wastewater treatment sludge from the production of toxaphene. Toxaphene 8001-35-2 0.0095 2.6 K042 Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5T. o-Dichlorobenzene 95-50-1 0.088 6.0 p-Dichlorobenzene 106-46-7 0.09 6.0 Pentachlorobenzene 608-93-5 0.055 10 1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14 1,2,4-Trichlorobenzene 120-82-1 0.055 19 K043 2,6-Dichlorophenol waste from the production of 2,4D. 2,4-Dichlorophenol 120-83-2 0.044 14 2,6-Dichlorophenol 187-65-0 0.044 14 2,4,5-Trichlorophenol 95-95-4 0.18 7.4 2,4,6-Trichlorophenol 88-06-2 0.035 7.4 2,3,4,6-Tetrachlorophenol 58-90-2 0.03 7.4 Pentachlorophenol 87-86-5 0.089 7.4 Tetrachloroethylene 127-18-4 0.056 6.0 HxCDDs (All Hexachlorodibenzo-p-dioxins) NA 0.000063 0.001 HxCDFs (All Hexachlorodibenzofurans) NA 0.000063 0.001 PeCDDs (All Pentachlorodibenzo-p-dioxins) NA 0.000063 0.001 PeCDFs (All Pentachlorodibenzofurans) NA 0.000035 0.001 TCDDs (All Tetrachlorodibenzo-p-dioxins) NA 0.000063 0.001 TCDFs (All Tetrachlorodibenzofurans) NA 0.000063 0.001 K097 Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane. Chlordane (alpha and gamma isomers) 57-74-9 0.0033 0.26 Heptachlor 76-44-8 0.0012 0.066 Heptachlor epoxide 1024-57-3 0.016 0.066 Hexachlorocyclopentadiene 77-47-4 0.057 2.4 K098 Untreated process wastewater from the production of toxaphene. Toxaphene 8001-35-2 0.0095 2.6 K099 Untreated wastewater from the production of 2,4-D. 2,4-Dichlorophenoxyacetic acid 94-75-7 0.72 10 HxCDDs (All Hexachlorodibenzo-p-dioxins) NA 0.000063 0.001 HxCDFs (All Hexachlorodibenzofurans) NA 0.000063 0.001 PeCDDs (All Pentachlorodibenzo-p-dioxins) NA 0.000063 0.001 PeCDFs (All Pentachlorodibenzofurans) NA 0.000035 0.001 TCDDs (All Tetrachlorodibenzo-p-dioxins) NA 0.000063 0.001 TCDFs (All Tetrachlorodibenzofurans) NA 0.000063 0.001 K123 Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salt. Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salt. NA CMBST; or CHOXD fb (BIODG or CARBN) CMBST K124 Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts. Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts. NA CMBST; or CHOXD fb (BIODG or CARBN) CMBST K125 Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts. Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts. NA CMBST; or CHOXD fb (BIODG or CARBN) CMBST K126 Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts. Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts. NA CMBST; or CHOXD fb (BIODG or CARBN) CMBST K131 Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide. Methyl bromide (Bromomethane) 74-83-9 0.11 15 K132 Spent absorbent and wastewater separator solids from the production of methyl bromide. Methyl bromide (Bromomethane) 74-83-9 0.11 15 Explosives: K044 Wastewater treatment sludges from the manufacturing and processing of explosives. Wastewater treatment sludges from the manufacturing and processing of explosives. NA DEACT DEACT K045 Spent carbon from the treatment of wastewater containing explosives. Spent carbon from the treatment of wastewater containing explosives. NA DEACT DEACT K046 Wastewater treatment sludges from the manufacturing formulation and loading of leadbased initiating compounds. Lead 7439-92-1 0.69 0.75 mg/L TCLP K047 Pink/red water from TNT operations. Pink/red water from TNT operations. NA DEACT DEACT Petroleum refining: K048 Dissolved air flotation (DAF) float from the petroleum refining industry. Benzene 71-43-2 0.14 10 Benzo(a)pyrene 50-32-8 0.061 3.4 bis(2-Ethylhexyl)phthalate 117-81-7 0.28 28 Chrysene 218-01-9 0.059 3.4 Di-n-butyl phthalate 84-74-2 0.057 28 Ethylbenzene 100-41-4 0.057 10 Fluorene 86-73-7 0.059 NA Naphthalene 91-20-3 0.059 5.6 Phenanthrene 85-01-8 0.059 5.6 Phenol 108-95-2 0.039 6.2 Pyrene 129-00-0 0.067 8.2 Toluene 108-88-33 0.08 10 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Lead 7439-92-1 0.69 NA Nickel 7440-02-0 NA 11 mg/L TCLP K049 Slop oil emulsion solids from the petroleum refining industry. Anthracene 120-12-7 0.059 3.4 Benzene 71-43-2 0.14 10 Benzo(a)pyrene 50-32-8 0.061 3.4 bis(2-Ethylhexyl)phthalate 117-81-7 0.28 28 Carbon disulfide 75-15-0 3.8 NA Chrysene 2218/01/09 0.059 3.4 2,4-Dimethylphenol 105-67-9 0.036 NA Ethylbenzene 100-41-4 0.057 10 Naphthalene 91-20-3 0.059 5.6 Phenanthrene 85-01-8 0.059 5.6 Phenol 108-95-2 0.039 6.2 Pyrene 129-00-0 0.067 8.2 Toluene 108-88-3 0.08 10 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 Cyanides (Total)7 57-12-5 1.2 590 Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 NA Nickel 7440-02-0 NA 11 mg/L TCLP K050 Heat exchanger bundle cleaning sludge from the petroleum refining industry. Benzo(a)pyrene 50-32-8 0.061 3.4 Phenol 108-95-2 0.039 6.2 Cyanides (Total)7 57-12-5 1.2 590 Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 NA Nickel 7440-02-0 NA 11 mg/L TCLP K051 API separator sludge from the petroleum refining industry. Acenaphthene 83-32-9 0.059 NA Anthracene 120-12-7 0.059 3.4 Benz(a)anthracene 56-55-3 0.059 3.4 Benzene 71-43-2 0.14 10 Benzo(a)pyrene 50-32-8 0.061 3.4 bis(2-Ethylhexyl)phthalate 117-81-7 0.28 28 Chrysene 2218/01/09 0.059 3.4 Di-n-butyl phthalate 105-67-9 0.057 28 Ethylbenzene 100-41-4 0.057 10 Fluorene 86-73-7 0.059 NA Naphthalene 91-20-3 0.059 5.6 Phenanthrene 85-01-8 0.059 5.6 Phenol 108-95-2 0.039 6.2 Pyrene 129-00-0 0.067 8.2 Toluene 108-88-3 0.08 10 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 Cyanides (Total)7 57-12-5 1.2 590 Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 NA Nickel 7440-02-0 NA 11 mg/L TCLP K052 Tank bottoms (leaded) from the petroleum refining industry. Benzene 71-43-2 0.14 10 Benzo(a)pyrene 50-32-8 0.061 3.4 o-Cresol 95-48-7 0.11 5.6 m-Cresol (difficult to distinguish from p-cresol) 108-39-4 0.77 5.6 p-Cresol (difficult to distinguish from m-cresol) 106-44-5 0.77 5.6 2,4-Dimethylphenol 105-67-9 0.036 NA Ethylbenzene 100-41-4 0.057 10 Naphthalene 91-20-3 0.059 5.6 Phenanthrene 85-01-8 0.059 5.6 Phenol 108-95-2 0.039 6.2 Toluene 108-88-3 0.08 10 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Lead 7439-92-1 0.69 NA Nickel 7440-02-0 NA 11 mg/L TCLP K169 Crude oil storage tank sediment from petroleum refining operations. Benz(a)anthracene 56-55-3 0.059 3.4 Benzene 71-43-2 0.14 10 Benzo(g,h,i)perylene 191-24-2 0.0055 1.8 Chrysene 218-01-9 0.059 3.4 Ethyl benzene 100-41-4 0.057 10 Fluorene 86-73-7 0.059 3.4 Naphthalene 91-20-3 0.059 5.6 Phenanthrene 81-05-8 0.059 5.6 Pyrene 129-00-0 0.067 8.2 Toluene (Methyl Benzene) 108-88-3 0.08 10 Xylene(s) (Total) 1330-20-7 0.32 30 K170 Clarified slurry oil tank sediment and/or in-line filter/separation solids from petroleum refining operations. Benz(a)anthracene 56-55-3 0.059 3.4 Benzene 71-43-2 0.14 10 Benzo(g,h,i)perylene 191-24-2 0.0055 1.8 Chrysene 218-01-9 0.059 3.4 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 Ethyl benzene 100-41-4 0.057 10 Fluorene 86-73-7 0.059 3.4 Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4 Naphthalene 91-20-3 0.059 5.6 Phenanthrene 81-05-8 0.059 5.6 Pyrene 129-00-0 0.067 8.2 Toluene (Methyl Benzene) 108-88-3 0.08 10 Xylene(s) (Total) 1330-20-7 0.32 30 K171 Spent Hydrotreating catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media). Benz(a)anthracene 56-55-3 0.059 3.4 Benzene 71-43-2 0.14 10 Chrysene 218-01-9 0.059 3.4 Ethyl benzene 100-41-4 0.057 10 Naphthalene 91-20-3 0.059 5.6 Phenanthrene 81-05-8 0.059 5.6 Pyrene 129-00-0 0.67 8.2 Toluene (Methyl Benzene) 108-88-3 0.08 10 Xylene(s) (Total) 1330-20-7 0.32 30 Arsenic 7740-38-2 1.4 5 mg/L TCLP Nickel 7440-02-0 3.98 11.0 mg/L TCLP Vanadium 7440-62-2 4.3 1.6 mg/L TCLP Reactive sulfides NA DEACT DEACT K172 Spent Hydrorefining catalyst from petroleum refining operations, including guard beds used to desulfurize feeds to other catalytic reactors (this listing does not include inert support media). Benzene 71-43-2 0.14 10 Ethyl benzene 100-41-4 0.57 10 Toluene (Methyl Benzene) 108-88-3 0.08 10 Xylene(s) (Total) 1330-20-7 0.32 30 Antimony 7740-36-0 1.9 1.15 mg/L TCLP Arsenic 7740-38-2 1.4 5 mg/L TCLP Nickel 7440-02-0 3.98 11.0 mg/L TCLP Vanadium 7440-62-2 4.3 1.6 mg/L TCLP Reactive sulfides NA DEACT DEACT Iron and steel: K061 Emission control dust/sludge from the primary production of steel in electric furnaces. Antimony 7440-36-0 NA 1.15 mg/L TCLP Arsenic 7440-38-2 NA 5.0 mg/L TCLP Barium 7440-39-3 NA 21 mg/L TCLP Beryllium 7440-41-7 NA 1.22 mg/L TCLP Cadmium 7440-43-9 0.69 0.11 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP Mercury 7439-97-6 NA 0.025 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP Selenium 7782-49-2 NA 5.7 mg/L TCLP Silver 7440-22-4 NA 0.14 mg/L TCLP Thallium 7440-28-0 NA 0.20 mg/L TCLP Zinc 7440-66-6 NA 4.3 mg/L TCLP K062 Spent pickle liquor generated by steel finishing operations within the iron and steel industry at steel works, blast furnaces (including coke ovens), rolling mills, iron and steel foundries, gray and ductile iron foundries, malleable iron foundries, steel investment foundries or other miscellaneous steel foundries or at facilities in the electrometallurgical products (except steel) industry, steel wiredrawing and steel nails and spikes industry, cold-rolled steel sheet, strip and bars industry, or steel pipe and tubes industry. Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP Nickel 7440-02-0 3.98 NA Primary aluminum: K088 Spent potliners from primary aluminum reduction. Acenaphthene 83-32-9 0.059 3.4 Anthracene 120-12-7 0.059 3.4 Benz(a)anthracene 56-55-3 0.059 3.4 Benzo(a)pyrene 50-32-8 0.061 3.4 Benzo(b)fluoranthene 205-99-2 0.11 6.8 Benzo(k)fluoranthene 207-08-9 0.11 6.8 Benzo(g,h,i)perylene 191-24-2 0.0055 1.8 Chrysene 218-01-9 0.059 3.4 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 Fluoranthene 206-44-0 0.068 3.4 Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4 Phenanthrene 85-01-8 0.059 5.6 Pyrene 129-00-0 0.067 8.2 Antimony 7440-36-0 1.9 1.15 mg/L TCLP Arsenic 7440-38-2 1.4 26.1 Barium 7440-39-3 1.2 21 mg/L TCLP Beryllium 7440-41-7 0.82 1.22 mg/L TCLP Cadmium 7440-43-9 0.69 0.11 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP Mercury 7439-97-6 0.15 0.025 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP Selenium 7782-49-2 0.82 5.7 mg/L TCLP Silver 7440-22-4 0.43 0.14 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Fluoride 16984-48-8 35 NA Secondary lead: K069 Emission control dust/sludge from secondary lead smelting, not including sludge generated from secondary acid scrubber systems. Treatment Subcategory 1 Calcium Sulfate (Low Lead) Cadmium 7440-43-9 0.69 0.11 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP Treatment Subcategory 2 Non- Calcium Sulfate (High Lead) Non- Calcium Sulfate (High Lead) NA NA RLEAD K100 Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting. Cadmium 7440-43-9 0.69 0.11 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Lead 7439-92-1 0.69 0.75 mg/L TCLP Veterinary pharmaceuticals: K084 Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds. Arsenic 7440-38-2 1.4 5.0 mg/L TCLP K101 Distillation tar residues from the distillation of anilinebased compounds in the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds. o-Nitroaniline 88-74-4 0.27 14 Arsenic 7440-38-2 1.4 5.0 mg/L TCLP Cadmium 7440-43-9 0.69 NA Lead 7439-92-1 0.69 NA Mercury 7439-97-6 0.15 NA K102 Residue from the use of activated carbon for decolourization in the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds. o-Nitrophenol 88-75-5 0.028 13 Arsenic 7440-38-2 1.4 5.0 mg/L TCLP Cadmium 7440-43-9 0.69 NA Lead 7439-92-1 0.69 NA Mercury 7439-97-6 0.15 NA Ink formulation: K086 Solvent washes and sludges, caustic washes and sludges, or water washes and sludges from cleaning tubs and equipment used in the formulation of ink from pigments, driers, soaps, and stabilizers containing chromium and lead. Acetone 67-64-1 0.28 160 Acetophenone 96-86-2 0.01 9.7 bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28 n-Butyl alcohol 71-36-3 5.6 2.6 Butyl benzyl phthalate 85-68-7 0.017 28 Cyclohexanone 108-94-1 0.36 NA o-Dichlorobenzene 95-50-1 0.088 6.0 Diethyl phthalate 84-66-2 0.2 28 Dimethyl phthalate 131-11-3 0.047 28 Di-n-butyl phthalate 84-74-2 0.057 28 Di-n-octyl phthalate 117-84-0 0.017 28 Ethyl acetate 141-78-6 0.34 33 Ethylbenzene 100-41-4 0.057 10 Methanol 67-56-1 5.6 NA Methyl ethyl ketone 78-93-3 0.28 36 Methyl isobutyl ketone 108-10-1 0.14 33 Methylene chloride 75-09-2 0.089 30 Naphthalene 91-20-3 0.059 5.6 Nitrobenzene 98-95-3 0.068 14 Toluene 108-88-3 0.08 10 1,1,1-Trichloroethane 71-55-6 0.054 6.0 Trichloroethylene 79-01-6 0.054 6.0 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Lead 7439-92-1 0.69 0.75 mg/L TCLP Coking: K060 Ammonia still lime sludge from coking operations. Benzene 71-43-2 0.14 10 Benzo(a)pyrene 50-32-8 0.061 3.4 Naphthalene 91-20-3 0.059 5.6 Phenol 108-95-2 0.039 6.2 Cyanides (Total)7 57-12-5 1.2 590 K087 Decanter tank tar sludge from coking operations. Acenaphthylene 208-96-8 0.059 3.4 Benzene 71-43-2 0.14 10 Chrysene 218-01-9 0.059 3.4 Fluoranthene 206-44-0 0.068 3.4 Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4 Naphthalene 91-20-3 0.059 5.6 Phenanthrene 85-01-8 0.059 5.6 Toluene 108-88-3 0.08 10 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 Lead 7439-92-1 0.69 0.75 mg/L TCLP K141 Process residues from the recovery of coal tar, including, but not limited to, collecting sump residues from the production of coke from coal or the recovery of coke by-products produced from coal. This listing does not include K087 (decanter tank tar sludges from coking operations). Benzene 71-43-2 0.14 10 Benz(a)anthracene 56-55-3 0.059 3.4 Benzo(a)pyrene 50-2-8 0.061 3.4 Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) 205-99-2 0.11 6.8 Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) 207-08-9 0.11 6.8 Chrysene 218-01-9 0.059 3.4 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4 K142 Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal. Benzene 71-43-2 0.14 10 Benz(a)anthracene 56-55-3 0.059 3.4 Benzo(a)pyrene 50-32-8 0.061 3.4 Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) 205-99-2 0.11 6.8 Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) 207-08-9 0.11 6.8 Chrysene 218-01-9 0.059 3.4 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4 K143 Process residues from the recovery of light oil, including, but not limited to, those generated in stills, decanters, and wash oil recovery units from the recovery of coke by-products produced from coal. Benzene 71-43-2 0.14 10 Benz(a)anthracene 56-55-3 0.059 3.4 Benzo(a)pyrene 50-32-8 0.061 3.4 Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) 205-99-2 0.11 6.8 Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) 207-08-9 0.11 6.8 Chrysene 218-01-9 0.059 3.4 K144 Wastewater sump residues from light oil refining, including, but not limited to, intercepting or contamination sump sludges from the recovery of coke by-products produced from coal. Benzene 71-43-2 0.14 10 Benz(a)pyrene 56-55-3 0.059 3.4 Benzo(a)anthracene 50-32-8 0.061 3.4 Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) 205-99-2 0.11 6.8 Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) 207-08-9 0.11 6.8 Chrysene 218-01-9 0.059 3.4 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 K145 Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal. Benzene 71-43-2 0.14 10 Benz(a)anthracene 56-55-3 0.059 3.4 Benzo(a)pyrene 50-32-8 0.061 3.4 Chrysene 218-01-9 0.059 3.4 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 Naphthalene 91-20-3 0.059 5.6 K147 Tar storage tank residues from coal tar refining. Benzene 71-43-2 0.14 10 Benz(a)anthracene 56-55-3 0.059 3.4 Benzo(a)pyrene 50-32-8 0.061 3.4 Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) 205-99-2 0.11 6.8 Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) 207-08-9 0.11 6.8 Chrysene 218-01-9 0.059 3.4 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4 K148 Residues from coal tar distillation, including but not limited to, still bottoms. Benz(a)anthracene 56-55-3 0.059 3.4 Benzo(a)pyrene 50-32-8 0.061 3.4 Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) 205-99-2 0.11 6.8 Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) 207-08-9 0.11 6.8 Chrysene 218-01-9 0.059 3.4 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4 Notes to Schedule 1: 1 Treatment subcategories are shown for some wastes. In these cases, it is necessary to identify the treatment subcategory that most closely describes the particular waste for which treatment is required. The land disposal treatment requirements for that waste are those shown for that treatment subcategory. 2 Haz. Waste Number means Hazardous Waste Number. These numbers are consistent with United States Environmental Protection Agency Hazardous Waste Numbers. If there is no United States Environmental Protection Agency Hazardous Waste Number for a waste, the Hazardous Waste Number is assigned to the waste by the Ontario Ministry of the Environment. 3 CAS Number means the Chemical Abstracts Service Registry Number. When the waste or a regulated constituent is described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only. 4 See Schedule 7 for a description of the treatment methods and treatment standards associated with each treatment code. In some cases, the entries in this Schedule may set out more than one treatment code for a regulated constituent. An entry may permit a choice of treatment methods. For example, the entry “CHOXD; BIODG; or CMBST” means that the waste may be treated using any of the treatment methods that are set out for those treatment codes in Schedule 7. An entry may require treatment methods to be applied in a particular sequence. For this purpose, the abbreviation “fb” means “followed by”. For example, the entry “CHOXD fb CARBN” means that the waste must first be treated using the treatment method that is set out for CHOXD in Schedule 7 and, following that treatment, it must be treated using the treatment method that is set out for CARBN in Schedule 7. An entry may combine a choice of treatment methods and a requirement to apply treatment methods in a particular sequence (for example, “(WETOX or CHOXD) fb CARBN; or CMBST”). 5 Concentration requirements for aqueous wastes are based on analysis of composite samples. 6 Concentration requirements for non-aqueous wastes are based on analysis of grab samples. 7 Both Cyanides (Total) and Cyanides (Amenable) for non-aqueous wastes are to be analyzed using Method 9010 or 9012, found in “Test Methods for Evaluating Solid Waste, Physical/ Chemical Methods”, United States Environmental Protection Agency Publication SW–846, with a sample size of 10 grams and a distillation time of one hour and 15 minutes. 7.1 The manufacturing of complete motor vehicles (body and chassis or unibody) or chassis only at a facility identified by NAICS code 336110 (Automobile and light-duty motor vehicle manufacturing), where “NAICS” means the North American Industry Classification System (NAICS) Canada 2012, dated January 2012 and maintained for Canada by Statistics Canada. 8 For these wastes, the treatment method described by the CMBST treatment code must be carried out at a facility that is authorized under an environmental compliance approval to treat these types of waste. 9 Resource Conservation and Recovery Act (RCRA), United States Congress, 42 U.S.C. s/s 6901 et seq. (1976), Subtitle C, Code of Federal Regulations, 40CFR, Chapter I - Environmental Protection Agency, Subchapter I - Solid Wastes, Part 261 - Identification and Listing of Hazardous Waste. 10 K175 non-aqueous wastes that have been treated in compliance with Schedule 1 land disposal treatment requirements must also be macroencapsulated in accordance with Schedule 8 (Alternative Treatment for Hazardous Debris), unless the waste is placed in: (1) A hazardous waste monofill containing only K175 wastes that meet all applicable Schedule 1 treatment standards; or (2) A dedicated hazardous waste landfill cell in which all other wastes being co-disposed are at pH≤ 6.0. O. Reg. 337/09, s. 20; O. Reg. 234/11, s. 40; O. Reg. 233/13, s. 1; O. Reg. 297/17, s. 2. SCHEDULE 1.1 EXEMPT HAZARDOUS INDUSTRIAL WASTES Industry and Site Waste ICI Canada Inc., Cornwall Brine purification muds (K071), saturator and clarifier sludges only, without mixing with other wastes or materials) generated from mercury cells at the chloralkali chlorine plant. Iron and steel industry, any site Sludge generated by lime stabilization of spent pickle liquor (K062) generated by steel finishing operations within the iron and steel industry at steel works, blast furnaces (including coke ovens), rolling mills, iron and steel foundries, gray and ductile iron foundries, malleable iron foundries, steel investment foundries or other miscellaneous steel foundries or at facilities in the electrometallurgical products (except steel) industry, steel wiredrawing and steel nails and spikes industry, cold-rolled steel sheet, strip and bars industry, or steel pipe and tubes industry. Iron and steel industry, any site Nonwastewater residues, such as slag, resulting from high temperature metals recovery (HTMR) processing of K061 or K062 waste, in units identified as rotary kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors, rotary hearth furnace/electric furnace combinations or industrial furnaces. Electroplating industry, any site Nonwastewater residues, such as slag, resulting from high temperature metals recovery (HTMR) processing of F006 waste, in units identified as rotary kilns, flame reactors, electric furnaces, plasma arc furnaces, slag reactors, rotary hearth furnace/electric furnace combinations or industrial furnaces. Organic chemical industry, any site Biological treatment sludge from the treatment of organic waste (K156) and wastewaters (K157) from the production of carbamates and carbamoyl oximes. Petroleum refining industry, any site Catalyst inert support media separated from spent hydrotreating catalyst (K171) or spent hydrorefining catalyst (K172). O. Reg. 461/05, s. 23. Schedule 2 Part A — Acute Hazardous Waste Chemical Acute Hazardous Waste Chemical Regulated Constituents (and Treatment Subcategories1) Land Disposal Treatment Requirements Aqueous Waste Non-aqueous Waste Column 1 Haz. Waste Number2 Column 2 CAS Number3 Column 3 Generic Name Column 4 Generic Name or other description Column 5 CAS Number3 Column 6 Treatment Code4 or Concentration5 (mg/L) Column 7 Treatment Code4 or Concentration6 (mg/kg, unless otherwise indicated) P026 5344-82-1 1-(o-Chlorophenyl)thiourea 1-(o-Chlorophenyl)thiourea 5344-82-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P081 55-63-0 1,2,3-Propanetriol, trinitrate Nitroglycerin 55-63-0 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST P042 51-43-4 1,2-Benzenediol,4-[1-hydroxy-2-(methylamino)ethyl]- Epinephrine 51-43-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P067 75-55-8 1,2-Propylenimine 2-Methyl-aziridine 75-55-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P185 26419-73-8 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O-[(methylamino)-carbonyl]oxime Tirpate 26419-73-8 BIODG; CARBN; CHOXD; CMBST or 0.056 CMBST or 0.28 P004 309-00-2 1,4,5,8-Dimethanonaphthalene,1,2,3,4,10,10-hexa-chloro-1,4,4a,5,8,8a,-hexahydro-, (1alpha,4alpha, 4abeta, 5alpha,8alpha,8abeta) Aldrin 309-00-2 0.021 0.066 P060 465-73-6 1,4,5,8-Dimethanonaphthalene,1,2,3,4,10,10-hexa-chloro-1,4,4a,5,8,8a-hexahydro-, (1alpha,4alpha, 4abeta, 5beta, 8beta, 8abeta)- Isodrin 465-73-6 0.021 0.066 P002 591-08-2 1-Acetyl-2-thiourea 1-Acetyl-2-thiourea 591-08-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P048 51-28-5 2,4-Dinitrophenol 2,4-Dinitrophenol 51-28-5 0.12 160 P051 72-20-8 2,7:3,6-Dimethanonaphth [2,3-b]oxirene, 3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-,(1aalpha,2beta,2abeta,3alpha,6alpha,6 abeta,7beta, 7aalpha)-, & metabolites Endrin 72-20-8 0.0028 0.13 Endrin aldehyde 7421-93-4 0.025 0.13 P037 60-57-1 2,7:3,6-Dimethanonaphth[2,3-b]oxirene,3,4,5,6,9,9-hexachloro-1a,2,2a,3,6,6a,7,7a-octahydro-, (1aalpha,2beta,2aalpha,3beta,6beta,6a alpha,7beta, 7aalpha)-[b]oxirene, 3,4,5,6,9,9-hexachloro- Dieldrin 60-57-1 0.017 0.13 P045 39196-18-4 2-Butanone,3,3-dimethyl-1-methylthio)-,O-[methylamino)carbonyl] oxime Thiofanox 39196-18-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P034 131-89-5 2-Cyclohexyl-4,6-dinitrophenol 2-Cyclohexyl-4,6-dinitrophenol 131-89-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P001 81-81-2 2H-1-Benzopyran-2-one, 4-hydroxy-3-(3-oxo-1-phenylbutyl)-, & salts, when present at concentrations greater than 0.3% Warfarin 81-81-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P069 75-86-5 2-Methyllactonitrile 2-Methyllactonitrile 75-86-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P017 598-31-2 2-Propanone, 1-bromo- Bromoacetone 598-31-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P005 107-18-6 2-Propen-1-ol Allyl alcohol 107-18-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P003 107-02-8 2-Propenal Acrolein 107-02-8 0.29 CMBST P102 107-19-7 2-Propyn-1-ol Propargyl alcohol 107-19-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P007 2763-96-4 3(2H)-Isoxazolone, 5-(aminomethyl)- 5-Aminomethyl 3-isoxazolol 2763-96-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P027 542-76-7 3-Chloropropionitrile 3-Chloropropionitrile 542-76-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P202 64-00-6 3-Isopropylphenyl N-methylcarbamate m-Cumenyl methylcarbamate 64-00-6 0.056 1.4 P047 534-52-1 4,6-Dinitro-o-cresol, & salts Treatment Subcategory 1 4,6-Dinitro-o-cresol: 4,6-Dinitro-o-cresol 543-52-1 0.28 160 Treatment Subcategory 2 4,6-Dinitro-o-cresol salts: 4,6-Dinitro-o-cresol salts NA (WETOX or CHOXD) fb CARBN; or CMBST CMBST P059 76-44-8 4,7-Methano-1H-indene, 1,4,5,6,7,8,8- heptachloro-3a,4,7,7a-tetrahydro- Heptachlor 76-44-8 0.0012 0.066 Heptachlor epoxide 1024-57-3 0.016 0.066 P008 504-24-5 4-Aminopyridine 4-Aminopyridine 504-24-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P008 504-24-5 4-Pyridinamine 4-Aminopyridine 504-24-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P007 2763-96-4 5-(Aminomethyl)-3-isoxazolol 5-Aminomethyl 3-isoxazolol 2763-96-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P050 115-29-7 6,9-Methano-2,4,3-benzodioxathiepin, 6,7,8,9, 10,10-hexachloro-1,5,5a,6,9,9a-hexahydro-, 3-oxide Endosulfan I 939-98-8 0.023 0.066 Endosulfan II 33213-6-5 0.029 0.13 Endosulfan sulfate 1031-07-8 0.029 0.13 P127 1563-66-2 7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-, methylcarbamate Carbofuran 1563-66-2 0.006 0.14 P088 145-73-3 7-Oxabicyclo[2.2.1]heptane-2,3-dicarboxylic acid Endothall 145-73-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P023 107-20-0 Acetaldehyde, chloro- Chloroacetaldehyde 107-20-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P057 640-19-7 Acetamide, 2-fluoro- Fluoroacetamide 640-19-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P002 591-08-2 Acetamide, N-(aminothioxomethyl)- 1-Acetyl-2-thiourea 591-08-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P058 62-74-8 Acetic acid, fluoro-, sodium salt Fluoroacetic acid, sodium salt 62-74-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P003 107-02-8 Acrolein Acrolein 107-02-8 0.29 CMBST P070 116-06-3 Aldicarb Aldicarb 116-06-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P203 1646-88-4 Aldicarb sulfone Aldicarb sulfone 1646-88-4 0.056 0.28 P004 309-00-2 Aldrin Aldrin 309-00-2 0.021 0.066 P005 107-18-6 Allyl alcohol Allyl alcohol 107-18-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P046 122-09-8 alpha,alpha-Dimethylphenethylamine alpha, alpha-Dimethylphenethylamine 122-09-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P072 86-88-4 alpha-Naphthylthiourea 1-Naphthyl-2-thiourea 86-88-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P006 20859-73-8 Aluminum phosphide Aluminum phosphide 20859-73-8 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST P009 131-74-8 Ammonium picrate Ammonium picrate 131-74-8 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST P119 7803-55-6 Ammonium vanadate Vanadium (measured in aqueous wastes only) 7440-62-2 4.3 STABL P099 506-61-6 Argentate(1-), bis(cyano-C)-, potassium Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Silver 7440-22-4 0.43 0.14 mg/L TCLP P010 7778-39-4 Arsenic acid H3AsO4 Arsenic 7440-38-2 1.4 5.0 mg/L TCLP P012 1327-53-3 Arsenic oxide As2O3 Arsenic 7440-38-2 1.4 5.0 mg/L TCLP P011 1303-28-2 Arsenic oxide As2O5 Arsenic 7440-38-2 1.4 5.0 mg/L TCLP P011 1303-28-2 Arsenic pentoxide Arsenic 7440-38-2 1.4 5.0 mg/L TCLP P012 1327-53-3 Arsenic trioxide Arsenic 7440-38-2 1.4 5.0 mg/L TCLP P038 692-42-2 Arsine, diethyl- Arsenic 7440-38-2 1.4 5.0 mg/L TCLP P036 696-28-6 Arsonous dichloride, phenyl- Arsenic 7440-38-2 1.4 5.0 mg/L TCLP P054 151-56-4 Aziridine Aziridine 151-56-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P067 75-55-8 Aziridine, 2-methyl- 2-Methyl-aziridine 75-55-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P013 542-62-1 Barium cyanide Barium 7440-39-3 NA 21 mg/L TCLP Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P024 106-47-8 Benzenamine, 4-chloro- p-Chloroaniline 106-47-8 0.46 16 P077 100-01-6 Benzenamine, 4-nitro- p-Nitroaniline 100-01-6 0.028 28 P028 100-44-7 Benzene, (chloromethyl)- Benzyl chloride 100-44-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P046 122-09-8 Benzeneethanamine, alpha,alpha-dimethyl- alpha, alpha-Dimethylphenethylamine 122-09-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P014 108-98-5 Benzenethiol Thiophenol (Benzene thiol) 108-98-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P188 57-64-7 Benzoic acid, 2-hydroxy-, compd. With (3aS-cis)-1,2,3,3a,8,8a-hexahydro-1,3a,8-trimethylpyrrolo[2,3-b]indol-5-yl methylcarbamate ester (1:1) Physostigmine salicylate 57-64-7 0.056 1.4 P028 100-44-7 Benzyl chloride Benzyl chloride 100-44-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P015 7440-41-7 Beryllium powder Beryllium 7440-41-7 RMETL; or RTHRM RMETL; or RTHRM P017 598-31-2 Bromoacetone Bromoacetone 598-31-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P018 357-57-3 Brucine Brucine 357-57-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P021 592-01-8 Calcium cyanide Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P021 592-01-8 Calcium cyanide Ca(CN)2 Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P189 55285-14-8 Carbamic acid, [(dibutylamino)-thio]methyl-, 2,3-dihydro-2,2-dimethyl- 7-benzofuranyl ester Carbosulfan 55285-14-8 0.028 1.4 P191 644-64-4 Carbamic acid, dimethyl-, 1-[(dimethyl-amino)carbonyl]- 5-methyl-1H- pyrazol-3-yl este Dimetilan 644-64-4 BIODG; CARBN; CHOXD; CMBST or 0.056 CMBST or 1.4 P190 1129-41-5 Carbamic acid, methyl-, 3-methylphenyl ester Metolcarb 1129-41-5 0.056 1.4 P192 119-38-0 Carbamic acid,dimethyl-,3-methyl-1-(1methylethyl)-1H-pyrazol-5-yl ester Isolan 119-38-0 BIODG; CARBN; CHOXD; CMBST or 0.056 CMBST or 1.4 P127 1563-66-2 Carbofuran Carbofuran 1563-66-2 0.006 0.14 P022 75-15-0 Carbon disulfide Carbon disulfide 75-15-0 3.8 CMBST or 4.8 mg/L TCLP P095 75-44-5 Carbonic dichloride Phosgene 75-44-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P189 55285-14-8 Carbosulfan Carbosulfan 55285-14-8 0.028 1.4 P023 107-20-0 Chloroacetaldehyde Chloroacetaldehyde 107-20-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P029 544-92-3 Copper cyanide Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P029 544-92-3 Copper cyanide Cu(CN) Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P030 NA Cyanides (soluble cyanide salts), not otherwise specified Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P031 460-19-5 Cyanogen Cyanogen 460-19-5 CHOXD: WETOX; or CMBST CHOXD: WETOX; or CMBST P033 506-77-4 Cyanogen chloride Cyanogen chloride 506-77-4 CHOXD: WETOX; or CMBST CHOXD: WETOX; or CMBST P033 506-77-4 Cyanogen chloride (CN)Cl Cyanogen chloride 506-77-4 CHOXD: WETOX; or CMBST CHOXD: WETOX; or CMBST P016 542-88-1 Dichloromethyl ether Dichloromethyl ether 542-88-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P036 696-28-6 Dichlorophenylarsine Arsenic 7440-38-2 1.4 5.0 mg/L TCLP P037 60-57-1 Dieldrin Dieldrin 60-57-1 0.017 0.13 P038 692-42-2 Diethylarsine Arsenic 7440-38-2 1.4 5.0 mg/L TCLP P041 311-45-5 Diethyl-p-nitrophenyl phosphate Diethyl-p-nitrophenyl phosphate 311-45-5 CARBN; or CMBST CMBST P043 55-91-4 Diisopropylfluorophosphate (DFP) Diisopropylfluorophosphate (DFP) 55-91-4 CARBN; or CMBST CMBST P044 60-51-5 Dimethoate Dimethoate 60-51-5 CARBN; or CMBST CMBST P191 644-64-4 Dimetilan Dimetilan 644-64-4 BIODG; CARBN; CHOXD; CMBST or 0.056 CMBST or 1.4 P020 88-85-7 Dinoseb 2-sec-Butyl-4,6-dinitrophenol (Dinoseb) 88-85-7 0.066 2.5 P085 152-16-9 Diphosphoramide, octamethyl- Octamethylpyrophosphoramide 152-16-9 CARBN; or CMBST CMBST P111 107-49-3 Diphosphoric acid, tetraethyl ester Tetraethylpyrophosphate 107-49-3 CARBN; or CMBST CMBST P039 298-04-4 Disulfoton Disulfoton 298-04-4 0.017 6.2 P049 541-53-7 Dithiobiuret Dithiobiuret 541-53-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P050 115-29-7 Endosulfan Endosulfan I 939-98-8 0.023 0.066 Endosulfan II 33213-6-5 0.029 0.13 Endosulfan sulfate 1031-07-8 0.029 0.13 P088 145-73-3 Endothall Endothall 145-73-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P051 72-20-8 Endrin Endrin 72-20-8 0.0028 0.13 Endrin aldehyde 7421-93-4 0.025 0.13 P051 72-20-8 Endrin, & metabolites Endrin 72-20-8 0.0028 0.13 Endrin aldehyde 7421-93-4 0.025 0.13 P042 51-43-4 Epinephrine Epinephrine 51-43-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P031 460-19-5 Ethanedinitrile Cyanogen 460-19-5 CHOXD: WETOX; or CMBST CHOXD: WETOX; or CMBST P194 23135-22-0 Ethanimidothioc acid, 2-(dimethylamino)-N-[[(methylamino)carbonyl]oxy]-2-oxo-, methyl ester Oxamyl 23135-22-0 0.056 0.28 P066 16752-77-5 Ethanimidothioic acid, N-[[(methylamino)carbonyl]oxy]-,methyl ester Methomyl 16752-77-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P101 107-12-0 Ethyl cyanide Ethyl cyanide (Propanenitrile) 107-12-0 0.24 360 P054 151-56-4 Ethyleneimine Aziridine 151-56-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P097 52-85-7 Famphur Famphur 52-85-7 0.017 15 P056 7782-41-4 Fluorine Fluoride (measured in aqueous wastes only) 16984-48-8 35 ADGAS fb NEUTR P057 640-19-7 Fluoroacetamide Fluoroacetamide 640-19-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P058 62-74-8 Fluoroacetic acid, sodium salt Fluoroacetic acid, sodium salt 62-74-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P198 23422-53-9 Formetanate hydrochloride Formetanate hydrochloride 23422-53-9 0.056 1.4 P197 17702-57-7 Formparanate Formparante 17702-57-7 BIODG; CARBN; CHOXD; CMBST or 0.056 CMBST or 1.4 P065 628-86-4 Fulminic acid, mercury(2+) salt Treatment Subcategory 1 Mercury fulminate non-aqueous wastes, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC: Mercury 7439-97-6 NA IMERC Treatment Subcategory 2 Mercury fulminate non-aqueous wastes that are either incinerator residues or are residues from RMERC; and contain greater than or equal to 260 mg/kg total mercury: Mercury 7439-97-6 NA RMERC Treatment Subcategory 3 Mercury fulminate non-aqueous wastes that are residues from RMERC and contain less than 260 mg/kg total mercury: Mercury 7439-97-6 NA 0.20 mg/L TCLP Treatment Subcategory 4 Mercury fulminate non-aqueous wastes that are incinerator residues and contain less than 260 mg/kg total mercury: Mercury 7439-97-6 NA 0.025 mg/L TCLP Treatment Subcategory 5 All mercury fulminate aqueous wastes: Mercury 7439-97-6 0.15 NA P059 76-44-8 Heptachlor Heptachlor 76-44-8 0.0012 0.066 Heptachlor epoxide 1024-57-3 0.016 0.066 P062 757-58-4 Hexaethyl tetraphosphate Hexaethyl tetraphosphate 757-58-4 CARBN; or CMBST CMBST P068 60-34-4 Hydrazine, methyl- Methyl hydrazine 60-34-4 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST P116 79-19-6 Hydrazinecarbothioamide Thiosemicarbazide 79-19-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P063 74-90-8 Hydrocyanic acid Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P063 74-90-8 Hydrogen cyanide Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P096 7803-51-2 Hydrogen phosphide Phosphine 7803-51-2 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST P060 465-73-6 Isodrin Isodrin 465-73-6 0.021 0.066 P192 119-38-0 Isolan Isolan 119-38-0 BIODG; CARBN; CHOXD; CMBST or 0.056 CMBST or 1.4 P196 15339-36-3 Manganese dimethyl dithiocarbamate Dithiocarbamates (total) NA BIODG; CARBN; CHOXD; CMBST or 0.028 CMBST or 28 P196 15339-36-3 Manganese,bis(dimethylcarbamodithioato-S,S')- Dithiocarbamates (total) NA BIODG; CARBN; CHOXD; CMBST or 0.028 CMBST or 28 P202 64-00-6 M-Cumenyl methylcarbamate m-Cumenyl methylcarbamate 64-00-6 0.056 1.4 P065 628-86-4 Mercury fulminate See Fulminic acid, mercury(2+) salt P092 62-38-4 Mercury, (acetato-O)phenyl- Treatment Subcategory 1 Phenyl mercuric acetate non-aqueous wastes, regardless of their total mercury content, that are not incinerator residues or are not residues from RMERC: Mercury 7439-97-6 NA IMERC; or RMERC Treatment Subcategory 2 Phenyl mercuric acetate non-aqueous wastes that are either incinerator residues or are residues from RMERC; and still contain greater than or equal to 260 mg/kg total mercury: Mercury 7439-97-6 NA RMERC Treatment Subcategory 3 Phenyl mercuric acetate non-aqueous wastes that are residues from RMERC and contain less than 260 mg/kg total mercury: Mercury 7439-97-6 NA 0.20 mg/L TCLP Treatment Subcategory 4 Phenyl mercuric acetate non-aqueous wastes that are incinerator residues and contain less than 260 mg/kg total mercury: Mercury 7439-97-6 NA 0.025 mg/L TCLP Treatment Subcategory 5 All phenyl mercuric acetate aqueous wastes: Mercury 7439-97-6 0.15 NA P082 62-75-9 Methanamine, N-methyl-N-nitroso- N-Nitrosodimethylamine 62-75-9 0.4 2.3 P064 624-83-9 Methane, isocyanato- Isocyanic acid, ethyl ester 624-83-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P016 542-88-1 Methane, oxybis[chloro- Dichloromethyl ether 542-88-1 (WETOX or CHOXD) fb CARBN;

or CMBST CMBST P112 509-14-8 Methane, tetranitro- Tetranitromethane 509-14-8 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST P118 75-70-7 Methanethiol, trichloro- Trichloromethanethiol 75-70-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P197 17702-57-7 Methanimidamide,N,N-dimethyl-N'-[2-methyl-4-[[(methylamino)carbonyl]oxy]phenyl]- Formparante 17702-57-7 BIODG; CARBN; CHOXD; CMBST or 0.056 CMBST or 1.4 P198 23422-53-9 Methanimidamide,N,N-dimethyl-N'-[3-[[(methylamino)-carbonyl]oxy]phenyl]-, monohydrochloride Formetanate hydrochloride 23422-53-9 0.056 1.4 P199 2032-65-7 Methiocarb Methiocarb 2032-65-7 0.056 1.4 P066 16752-77-5 Methomyl Methomyl 16752-77-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P068 60-34-4 Methyl hydrazine Methyl hydrazine 60-34-4 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST P064 624-83-9 Methyl isocyanate Isocyanic acid, ethyl ester 624-83-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P071 298-00-0 Methyl parathion Methyl parathion 298-00-0 0.014 4.6 P190 1129-41-5 Metolcarb Metolcarb 1129-41-5 0.056 1.4 P128 315-18-4 Mexacarbate Mexacarbate 315-18-4 0.056 1.4 P073 13463-39-3 Nickel carbonyl Nickel 7440-02-0 3.98 11 mg/L TCLP P073 13463-39-3 Nickel carbonyl Ni(CO)4,(T-4)- Nickel 7440-02-0 3.98 11 mg/L TCLP P074 557-19-7 Nickel cyanide Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Nickel 7440-02-0 3.98 11 mg/L TCLP P074 557-19-7 Nickel cyanide Ni(CN)2 Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Nickel 7440-02-0 3.98 11 mg/L TCLP P075 54-11-5 Nicotine, & salts Nicotine and salts 54-11-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P076 10102-43-9 Nitric oxide Nitric oxide 10102-43-9 ADGAS ADGAS P078 10102-44-0 Nitrogen dioxide Nitrogen dioxide 10102-44-0 ADGAS ADGAS P076 10102-43-9 Nitrogen oxide NO Nitric oxide 10102-43-9 ADGAS ADGAS P078 10102-44-0 Nitrogen oxide NO2 Nitrogen dioxide 10102-44-0 ADGAS ADGAS P081 55-63-0 Nitroglycerine Nitroglycerin 55-63-0 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST P082 62-75-9 N-Nitrosodimethylamine N-Nitrosodimethylamine 62-75-9 0.4 2.3 P084 4549-40-0 N-Nitrosomethylvinylamine N-Nitrosomethylvinylamine 4549-40-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P040 297-97-2 O,O-Diethyl O-pyrazinyl phosphorothioate 0,0-Diethyl O-pyrazinyl phosphorothioate 297-97-2 CARBN; or CMBST CMBST P085 152-16-9 Octamethylpyrophosphoramide Octamethylpyrophosphoramide 152-16-9 CARBN; or CMBST CMBST P087 20816-12-0 Osmium oxide OsO4,(T-4)- Osmium tetroxide 20816-12-0 RMETL; or RTHRM RMETL; or RTHRM P087 20816-12-0 Osmium tetroxide Osmium tetroxide 20816-12-0 RMETL; or RTHRM RMETL; or RTHRM P194 23135-22-0 Oxamyl Oxamyl 23135-22-0 0.056 0.28 P089 56-38-2 Parathion Parathion 56-38-2 0.014 4.6 P024 106-47-8 p-Chloroaniline p-Chloroaniline 106-47-8 0.46 16 P020 88-85-7 Phenol, 2-(1-methylpropyl)-4,6-dinitro- 2-sec-Butyl-4,6-dinitrophenol (Dinoseb) 88-85-7 0.066 2.5 P009 131-74-8 Phenol, 2,4,6-trinitro-, ammonium salt Ammonium picrate 131-74-8 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST P048 51-28-5 Phenol, 2,4-dinitro- 2,4-Dinitrophenol 51-28-5 0.12 160 P034 131-89-5 Phenol, 2-cyclohexyl-4,6-dinitro- 2-Cyclohexyl-4,6-dinitrophenol 131-89-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P047 534-52-1 Phenol, 2-methyl-4,6-dinitro-, & salts See 4,6-Dinitro-o-cresol, & salts P202 64-00-6 Phenol, 3-(1-methylethyl)-, methyl carbamate m-Cumenyl methylcarbamate 64-00-6 0.056 1.4 P201 2631-37-0 Phenol, 3-methyl-5-(1-methylethyl)-,methyl carbamate Promecarb 2631-37-0 0.056 1.4 P199 2032-65-7 Phenol,(3,5-dimethyl-4-(methylthio)-,methylcarbamate Methiocarb 2032-65-7 0.056 1.4 P128 315-18-4 Phenol,4-(dimethylamino)-3,5-dimethyl-, methylcarbamate (ester) Mexacarbate 315-18-4 0.056 1.4 P092 62-38-4 Phenylmercury acetate See Mercury, (acetato-O)phenyl- P093 103-85-5 Phenylthiourea Phenylthiourea 103-85-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P094 298-02-2 Phorate Phorate 298-02-2 0.021 4.6 P095 75-44-5 Phosgene Phosgene 75-44-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P096 7803-51-2 Phosphine Phosphine 7803-51-2 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST P041 311-45-5 Phosphoric acid, diethyl 4-nitrophenyl ester Diethyl-p-nitrophenyl phosphate 311-45-5 CARBN; or CMBST CMBST P094 298-02-2 Phosphorodithioic acid, O,O-diethyl S-[(ethylthio)methyl] ester Phorate 298-02-2 0.021 4.6 P039 298-04-4 Phosphorodithioic acid, O,O-diethyl S-[2-(ethylthio)ethyl] ester Disulfoton 298-04-4 0.017 6.2 P044 60-51-5 Phosphorodithioic acid,O,O-dimethylS-[2-(methylamino)-2-oxoethyl] ester Dimethoate 60-51-5 CARBN; or CMBST CMBST P043 55-91-4 Phosphorofluoridic acid, bis(1-methylethyl) ester Diisopropylfluorophosphate (DFP) 55-91-4 CARBN; or CMBST CMBST P071 298-00-0 Phosphorothioic acid, O,O,-dimethyl O-(4-nitrophenyl) ester Methyl parathion 298-00-0 0.014 4.6 P089 56-38-2 Phosphorothioic acid, O,O-diethyl O-(4-nitrophenyl) ester Parathion 56-38-2 0.014 4.6 P040 297-97-2 Phosphorothioic acid, O,O-diethyl O-pyrazinyl ester 0,0-Diethyl O-pyrazinyl phosphorothioate 297-97-2 CARBN; or CMBST CMBST P097 52-85-7 Phosphorothioic acid, O-[4-[(dimethylamino)sulfonyl]phenyl] O,O-r dimethyl ester Famphur 52-85-7 0.017 15 P188 57-64-7 Physostigmine salicylate. Physostigmine salicylate 57-64-7 0.056 1.4 P204 57-47-6 Physostigmine. Physostigmine 57-47-6 0.056 1.4 P110 78-00-2 Plumbane, tetraethyl- Lead 7439-92-1 0.69 0.75 mg/L TCLP P077 100-01-6 p-Nitroaniline p-Nitroaniline 100-01-6 0.028 28 P098 151-50-8 Potassium cyanide Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P098 151-50-8 Potassium cyanide K(CN) Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P099 506-61-6 Potassium silver cyanide Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Silver 7440-22-4 0.43 0.14 mg/L TCLP P201 2631-37-0 Promecarb Promecarb 2631-37-0 0.056 1.4 P203 1646-88-4 Propanal,2-methyl-2-(methyl-sulfonyl)-,O-[(methylamino)carbonyl] oxime Aldicarb sulfone 1646-88-4 0.056 0.28 P070 116-06-3 Propanal,2-methyl-2-(methylthio)-,O-[(methylamino)carbonyl]oxime Aldicarb 116-06-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P101 107-12-0 Propanenitrile Ethyl cyanide (Propanenitrile) 107-12-0 0.24 360 P069 75-86-5 Propanenitrile, 2-hydroxy-2-methyl- 2-Methyllactonitrile 75-86-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P027 542-76-7 Propanenitrile, 3-chloro- 3-Chloropropionitrile 542-76-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P102 107-19-7 Propargyl alcohol Propargyl alcohol 107-19-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P075 54-11-5 Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)-, & salts Nicotine and salts 54-11-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P204 57-47-6 Pyrrolo[2,3-b]indol-5-ol,1,2,3,3a,8,8a-hexahydro-1,3a,8- trimethyl-,methylcarbamate (ester),(3aS-cis)- Physostigmine 57-47-6 0.056 1.4 P114 12039-52-0 Selenious acid, dithallium(1+) salt Selenium 7782-49-2 0.82 5.7 mg/L TCLP P103 630-10-4 Selenourea Selenium 7782-49-2 0.82 5.7 mg/L TCLP P104 506-64-9 Silver cyanide Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Silver 7440-22-4 0.43 0.14 mg/L TCLP P104 506-64-9 Silver cyanide Ag(CN) Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 Silver 7440-22-4 0.43 0.14 mg/L TCLP P105 26628-22-8 Sodium azide Sodium azide 26628-22-8 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST P106 143-33-9 Sodium cyanide Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P106 143-33-9 Sodium cyanide Na(CN) Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P108 57-24-9 Strychnidin-10-one, & salts Strychnine and salts 57-24-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P018 357-57-3 Strychnidin-10-one, 2,3-dimethoxy- Brucine 357-57-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P108 57-24-9 Strychnine, & salts Strychnine and salts 57-24-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P115 7446-18-6 Sulfuric acid, dithallium(1+) salt Thallium (measured in aqueous wastes only) 7440-28-0 1.4 RTHRM; or STABL P110 78-00-2 Tetraethyl lead Lead 7439-92-1 0.69 0.75 mg/L TCLP P111 107-49-3 Tetraethyl pyrophosphate Tetraethylpyrophosphate 107-49-3 CARBN; or CMBST CMBST P109 3689-24-5 Tetraethyldithiopyrophosphate Tetraethyldithiopyrophosphate 3689-24-5 CARBN; or CMBST CMBST P112 509-14-8 Tetranitromethane Tetranitromethane 509-14-8 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST P062 757-58-4 Tetraphosphoric acid, hexaethyl ester Hexaethyl tetraphosphate 757-58-4 CARBN; or CMBST CMBST P113 1314-32-5 Thallic oxide Thallium (measured in aqueous wastes only) 7440-28-0 1.4 RTHRM; or STABL P113 1314-32-5 Thallium oxide Tl2O3 Thallium (measured in aqueous wastes only) 7440-28-0 1.4 RTHRM; or STABL P114 12039-52-0 Thallium(I) selenite Selenium 7782-49-2 0.82 5.7 mg/L TCLP P115 7446-18-6 Thallium(I) sulfate Thallium (measured in aqueous wastes only) 7440-28-0 1.4 RTHRM; or STABL P109 3689-24-5 Thiodiphosphoric acid, tetraethyl ester Tetraethyldithiopyrophosphate 3689-24-5 CARBN; or CMBST CMBST P045 39196-18-4 Thiofanox Thiofanox 39196-18-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P049 541-53-7 Thioimidodicarbonic diamide [(H2N)C(S)]2NH Dithiobiuret 541-53-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P014 108-98-5 Thiophenol Thiophenol (Benzene thiol) 108-98-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P116 79-19-6 Thiosemicarbazide Thiosemicarbazide 79-19-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P026 5344-82-1 Thiourea, (2-chlorophenyl)- 1-(o-Chlorophenyl)thiourea 5344-82-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P072 86-88-4 Thiourea, 1-naphthalenyl- 1-Naphthyl-2-thiourea 86-88-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P093 103-85-5 Thiourea, phenyl- Phenylthiourea 103-85-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P185 26419-73-8 Tirpate Tirpate 26419-73-8 BIODG; CARBN; CHOXD; CMBST or 0.056 CMBST or 0.28 P123 8001-35-2 Toxaphene Toxaphene 8001-35-2 0.0095 2.6 P118 75-70-7 Trichloromethanethiol Trichloromethanethiol 75-70-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P119 7803-55-6 Vanadic acid, ammonium salt Vanadium (measured in aqueous wastes only)) 7440-62-2 4.3 STABL P120 1314-62-1 Vanadium oxide, V2O5 Vanadium (measured in aqueous wastes only) 7440-62-2 4.3 STABL P120 1314-62-1 Vanadium pentoxide Vanadium (measured in aqueous wastes only) 7440-62-2 4.3 STABL P084 4549-40-0 Vinylamine, N-methyl-N-nitroso- N-Nitrosomethylvinylamine 4549-40-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P001 81-81-2 Warfarin, & salts, when present at concentrations greater than 0.3% Warfarin 81-81-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST P121 557-21-1 Zinc cyanide Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P121 557-21-1 Zinc cyanide Zn(CN)2 Cyanides (Total)7 57-12-5 1.2 590 Cyanides (Amenable)7 57-12-5 0.86 30 P122 1314-84-7 Zinc phosphide Zn3P2, when present at concentrations greater than 10% Zinc Phosphide 1314-84-7 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST P205 137-30-4 Zinc, bis(dimethylcarbamodithioato-S,S')- Dithiocarbamates (total) NA 0.028 28 P205 137-30-4 Ziram Dithiocarbamates (total) NA 0.028 28 Notes to Part A of Schedule 2: 1 Treatment subcategories are shown for some wastes. In these cases, it is necessary to identify the treatment subcategory that most closely describes the particular waste for which treatment is required. The land disposal treatment requirements for that waste are those shown for that treatment subcategory. 2 Haz. Waste Number means Hazardous Waste Number. These numbers are consistent with United States Environmental Protection Agency Hazardous Waste Numbers. If there is no United States Environmental Protection Agency Hazardous Waste Number for a waste, the Hazardous Waste Number is assigned to the waste by the Ontario Ministry of the Environment. 3 CAS Number means the Chemical Abstracts Service Registry Number. When the waste or a regulated constituent is described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only. 4 See Schedule 7 for a description of the treatment methods and treatment standards associated with each treatment code. In some cases, the entries in this Schedule may set out more than one treatment code for a regulated constituent. An entry may permit a choice of treatment methods. For example, the entry “CHOXD; BIODG; or CMBST” means that the waste may be treated using any of the treatment methods that are set out for those treatment codes in Schedule 7. An entry may require treatment methods to be applied in a particular sequence. For this purpose, the abbreviation “fb” means “followed by”. For example, the entry “CHOXD fb CARBN” means that the waste must first be treated using the treatment method that is set out for CHOXD in Schedule 7 and, following that treatment, it must be treated using the treatment method that is set out for CARBN in Schedule 7. An entry may combine a choice of treatment methods and a requirement to apply treatment methods in a particular sequence (for example, “(WETOX or CHOXD) fb CARBN; or CMBST”). 5 Concentration requirements for aqueous wastes are based on analysis of composite samples. 6 Concentration requirements for non-aqueous wastes are based on analysis of grab samples. 7 Both Cyanides (Total) and Cyanides (Amenable) for non-aqueous wastes are to be analyzed using Method 9010 or 9012, found in “Test Methods for Evaluating Solid Waste, Physical/ Chemical Methods”, United States Environmental Protection Agency Publication SW–846, with a sample size of 10 grams and a distillation time of one hour and 15 minutes. Schedule 2 Part B — Hazardous Waste Chemical Hazardous Waste Chemical Regulated Constituents (and Treatment Subcategories1) Land Disposal Treatment Requirements Aqueous Waste Non-aqueous Waste Column 1 Haz. Waste Number2 Column 2 CAS Number3 Column 3 Generic Name Column 4 Generic Name or other description Column 5 CAS Number3 Column 6 Treatment Code4 or Concentration5 (mg/L) Column 7 Treatment Code4 or Concentration6 (mg/kg, unless otherwise indicated) U021 92-87-5 [1,1-Biphenyl]-4,4-diamine Benzidine 92-87-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U073 91-94-1 [1,1'-Biphenyl]-4,4'-diamine, 3,3'-dichloro- 3,3'-Dichlorobenzidine 91-94-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U091 119-90-4 [1,1'-Biphenyl]-4,4'-diamine, 3,3'-dimethoxy- 3,3'-Dimethoxybenzidine 119-90-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U095 119-93-7 [1,1'-Biphenyl]-4,4'-diamine, 3,3'-dimethyl- 3,3'-Dimethylbenzidine 119-93-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U208 630-20-6 1,1,1,2-Tetrachloroethane 1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0 U209 79-34-5 1,1,2,2-Tetrachloroethane 1,1,2,2-Tetrachloroethane 79-34-5 0.057 6.0 U227 79-00-5 1,1,2-Trichloroethane 1,1,2-Trichloroethane 79-00-5 0.054 6.0 U078 75-35-4 1,1-Dichloroethylene 1,1-Dichloroethylene 75-35-4 0.025 6.0 U098 57-14-7 1,1-Dimethylhydrazine 1,1-Dimethylhydrazine 57-14-7 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U207 95-94-3 1,2,4,5-Tetrachlorobenzene 1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14 U085 1464-53-5 1,2:3,4-Diepoxybutane 1,2:3,4-Diepoxybutane 1464-53-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U069 84-74-2 1,2-Benzenedicarboxylic acid, dibutyl ester Di-n-butyl phthalate 84-74-2 0.057 28 U088 84-66-2 1,2-Benzenedicarboxylic acid, diethyl ester Diethyl phthalate 84-66-2 0.20 28 U102 131-11-3 1,2-Benzenedicarboxylic acid, dimethyl ester Dimethyl phthalate 131-11-3 0.047 28 U107 117-84-0 1,2-Benzenedicarboxylic acid, dioctyl ester Di-n-octyl phthalate 117-84-0 0.017 28 U028 117-81-7 1,2-Benzenedicarboxylic acid,bis(2-ethylhexyl) ester bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28 U202 81-07-2 1,2-Benzisothiazol-3(2H)-one, 1,1-dioxide, & salts Saccharin 81-07-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U066 96-12-8 1,2-Dibromo-3-chloropropane 1,2-Dibromo-3-chloropropane 96-12-8 0.11 15 U079 156-60-5 1,2-Dichloroethylene trans-1,2-Dichloroethylene 156-60-5 0.054 30 U099 540-73-8 1,2-Dimethylhydrazine 1,2-Dimethylhydrazine 540-73-8 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U109 122-66-7 1,2-Diphenylhydrazine 1,2-Diphenylhydrazine 122-66-7 CHOXD; CHRED; CARBN; BIODG; CMBST or 0.087 CHOXD; CHRED; or CMBST U155 91-80-5 1,2-Ethanediamine,N,N-dimethyl-N'-2-pyridinyl-N'-(2-thienylmethyl)- Methapyrilene 91-80-5 0.081 1.5 U193 1120-71-4 1,2-Oxathiolane, 2,2-dioxide 1,3-Propane sultone 1120-71-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U142 143-50-0 1,3,4-Metheno-2H-cyclobuta[cd]pentalen-2-one, 1,1a,3,3a,4,5,5,5a,5b,6-decachlorooctahydro- Kepone 143-50-0 0.0011 0.13 U234 99-35-4 1,3,5-Trinitrobenzene 1,3,5-Trinitrobenzene 99-35-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U182 123-63-7 1,3,5-Trioxane, 2,4,6-trimethyl- Paraldehyde 123-63-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U201 108-46-3 1,3-Benzenediol Resorcinol 108-46-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U364 22961-82-6 1,3-Benzodioxol-4-ol, 2,2-dimethyl-, Bendiocarb phenol 22961-82-6 BIODG; CARBN; CHOXD; CMBST or 0.056 CMBST or 1.4 U278 22781-23-3 1,3-Benzodioxol-4-ol, 2,2-dimethyl-,methyl carbamate Bendiocarb 22781-23-3 0.056 1.4 U141 120-58-1 1,3-Benzodioxole, 5-(1-propenyl)- Isosafrole 120-58-1 0.081 2.6 U203 94-59-7 1,3-Benzodioxole, 5-(2-propenyl)- Safrole 94-59-7 0.081 22 U090 94-58-6 1,3-Benzodioxole, 5-propyl- Dihydrosafrole 94-58-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U128 87-68-3 1,3-Butadiene, 1,1,2,3,4,4-hexachloro- Hexachlorobutadiene 87-68-3 0.055 5.6 U130 77-47-4 1,3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro- Hexachlorocyclopentadiene 77-47-4 0.057 2.4 U084 542-75-6 1,3-Dichloropropene cis-1,3-Dichloropropylene 10061-01-5 0.036 18 trans-1,3-Dichloropropylene 10061-02-6 0.036 18 U190 85-44-9 1,3-Isobenzofurandione Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) 100-21-0; 85-44-9 0.055 28 U186 504-60-9 1,3-Pentadiene 1,3-Pentadiene 504-60-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U193 1120-71-4 1,3-Propane sultone 1,3-Propane sultone 1120-71-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U074 764-41-0 1,4-Dichloro-2-butene cis,1,4-Dichloro-2-butene 1476-11-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST trans-1,4-Dichloro-2-butene 764-41-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U108 123-91-1 1,4-Diethyleneoxide 1,4-Dioxane 123-91-1 (WETOX or CHOXD) fb CARBN; or CMBST or 12 CMBST or 170 U108 123-91-1 1,4-Dioxane 1,4-Dioxane 123-91-1 (WETOX or CHOXD) fb CARBN; or CMBST or 12 CMBST or 170 U166 130-15-4 1,4-Naphthalenedione 1,4-Naphthoquinone 130-15-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U166 130-15-4 1,4-Naphthoquinone 1,4-Naphthoquinone 130-15-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U172 924-16-3 1-Butanamine, N-butyl-N-nitroso- N-Nitroso-di-n-butylamine 924-16-3 0.04 17 U031 71-36-3 1-Butanol n-Butyl alcohol 71-36-3 5.6 2.6 U011 61-82-5 1H-1,2,4-Triazol-3-amine Amitrole 61-82-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U186 504-60-9 1-Methylbutadiene 1,3-Pentadiene 504-60-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U167 134-32-7 1-Naphthalenamine 1-Naphthylamine 134-32-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U279 63-25-2 1-Naphthalenol, methylcarbamate Carbaryl 63-25-2 0.006 0.14 U194 107-10-8 1-Propanamine n-Propylamine 107-10-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U111 621-64-7 1-Propanamine, N-nitroso-N-propyl- Di-n-propylnitrosamine 621-64-7 0.40 14 U110 142-84-7 1-Propanamine, N-propyl- Dipropylamine 142-84-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U235 126-72-7 1-Propanol, 2,3-dibromo-, phosphate (3:1) Tris(2,3-Dibromopropyl) phosphate 126-72-7 0.11 0.10 U140 78-83-1 1-Propanol, 2-methyl- Isobutyl alcohol 78-83-1 5.6 170 U243 1888-71-7 1-Propene, 1,1,2,3,3,3-hexachloro- Hexachloropropylene 1888-71-7 0.035 30 U084 542-75-6 1-Propene, 1,3-dichloro- cis-1,3-Dichloropropylene 10061-01-5 0.036 18 trans-1,3-Dichloropropylene 10061-02-6 0.036 18 U085 1464-53-5 2,2-Bioxirane 1,2:3,4-Diepoxybutane 1464-53-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST See F027 58-90-2 2,3,4,6-Tetrachlorophenol See F027 in Schedule 1 U237 66-75-1 2,4-(1H,3H)-Pyrimidinedione, 5-[bis(2-chloroethyl)amino]- Uracil mustard 66-75-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST See F027 93-76-5 2,4,5-T See F027 in Schedule 1 See F027 95-95-4 2,4,5-Trichlorophenol See F027 in Schedule 1 See F027 88-06-2 2,4,6-Trichlorophenol See F027 in Schedule 1 U240 94-75-7 2,4-D, salts & esters Treatment Subcategory 1 2,4-D (2,4-Dichlorophenoxyacetic acid): 2,4-D(2,4-Dichlorophenoxyacetic acid) 94-75-7 0.72 10 Treatment Subcategory 2 2,4-D (2,4-Dichlorophenoxyacetic acid) salts and esters: 2,4-D (2,4-Dichlorophenoxyacetic acid) salts and esters NA (WETOX or CHOXD) fb CARBN; or CMBST CMBST U081 120-83-2 2,4-Dichlorophenol 2,4-Dichlorophenol 120-83-2 0.044 14 U101 105-67-9 2,4-Dimethylphenol 2,4-Dimethylphenol 105-67-9 0.036 14 U105 121-14-2 2,4-Dinitrotoluene 2,4-Dinitrotoluene 121-14-2 0.32 140 U197 106-51-4 2,5-Cyclohexadiene-1,4-dione p-Benzoquinone 106-51-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U147 108-31-6 2,5-Furandione Maleic anhydride 108-31-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U082 87-65-0 2,6-Dichlorophenol 2,6-Dichlorophenol 87-65-0 0.044 14 U106 606-20-2 2,6-Dinitrotoluene 2,6-Dinitrotoluene 606-20-2 0.55 28 U236 72-57-1 2,7-Naphthalenedisulfonic acid, 3,3'-[(3,3'-dimethyl[1,1'-biphenyl]-4,4'-diyl)bis(azo)bis[5-amino-4-hydroxy]-,tetrasodium salt Trypan Blue 72-57-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U005 53-96-3 2-Acetylaminofluorene 2-Acetylaminofluorene 53-96-3 0.059 140 U159 78-93-3 2-Butanone Methyl ethyl ketone 78-93-3 0.28 36 U160 1338-23-4 2-Butanone, peroxide Methyl ethyl ketone peroxide 1338-23-4 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U053 4170-30-3 2-Butenal Crotonaldehyde 4170-30-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U074 764-41-0 2-Butene, 1,4-dichloro- cis,1,4-Dichloro-2-butene 1476-11-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST trans-1,4-Dichloro-2-butene 764-41-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U143 303-34-4 2-Butenoic acid, 2-methyl-, 7-[[2,3-dihydroxy-2-(1-methoxyethyl)-3-methyl-1-oxobutoxy]methyl]-2,3,5,7a-tetrahydro-1H-pyrrolizin-1-yl ester,[1S-[1alpha(Z),7(2S*,3R*), 7aalpha]]- Lasiocarpine 303-34-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U042 110-75-8 2-Chloroethyl vinyl ether 2-Chloroethyl vinyl ether 110-75-8 0.062 CMBST U125 98-01-1 2-Furancarboxaldehyde Furfural 98-01-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U058 50-18-0 2H-1,3,2-Oxazaphosphorin-2-amine,N,N-bis(2-chloroethyl)tetrahydro-, 2-oxide Cyclophosphamide 50-18-0 CARBN; or CMBST CMBST U248 81-81-2 2H-1-Benzopyran-2-one,4-hydroxy-3-(3-oxo-1-phenyl-butyl)-, & salts, when present at concentrations of 0.3% or less Warfarin 81-81-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U116 96-45-7 2-Imidazolidinethione Ethylene thiourea 96-45-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U168 91-59-8 2-Naphthalenamine 2-Naphthylamine 91-59-8 0.52 CMBST U171 79-46-9 2-Nitropropane 2-Nitropropane 79-46-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U191 109-06-8 2-Picoline 2-Picoline 109-06-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U002 67-64-1 2-Propanone Acetone 67-64-1 0.28 160 U007 79-06-1 2-Propenamide Acrylamide 79-06-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U009 107-13-1 2-Propenenitrile Acrylonitrile 107-13-1 0.24 84 U152 126-98-7 2-Propenenitrile, 2-methyl- Methacrylonitrile 126-98-7 0.24 84 U008 79-10-7 2-Propenoic acid Acrylic acid 79-10-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U118 97-63-2 2-Propenoic acid, 2-methyl-, ethyl ester Ethyl methacrylate 97-63-2 0.14 160 U162 80-62-6 2-Propenoic acid, 2-methyl-, methyl ester Methyl methacrylate 80-62-6 0.14 160 U113 140-88-5 2-Propenoic acid, ethyl ester Ethyl acrylate 140-88-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U073 91-94-1 3,3'-Dichlorobenzidine 3,3'-Dichlorobenzidine 91-94-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U091 119-90-4 3,3'-Dimethoxybenzidine 3,3'-Dimethoxybenzidine 119-90-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U095 119-93-7 3,3'-Dimethylbenzidine 3,3'-Dimethylbenzidine 119-93-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U148 123-33-1 3,6-Pyridazinedione, 1,2-dihydro- Maleic hydrazide 123-33-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U157 56-49-5 3-Methylcholanthrene 3-Methylcholanthrene 56-49-5 0.0055 15 U164 56-04-2 4(1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-thioxo- Methylthiouracil 56-04-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U158 101-14-4 4,4'-Methylenebis(2-chloroaniline) 4,4'-Methylene bis(2-chloroaniline) 101-14-4 0.50 30 U036 57-74-9 4,7-Methano-1H-indene, 1,2,4,5,6,7,8,8-octachloro-2,3,3a,4,7,7a-hexahydro- Chlordane (alpha and gamma isomers) 57-74-9 0.0033 0.26 U030 101-55-3 4-Bromophenyl phenyl ether 4-Bromophenyl phenyl ether 101-55-3 0.055 15 U049 3165-93-3 4-Chloro-o-toluidine, hydrochloride 4-Chloro-o-toluidine hydrochloride 3165-93-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U161 108-10-1 4-Methyl-2-pentanone Methyl isobutyl ketone 108-10-1 0.14 33 U059 20830-81-3 5,12-Naphthacenedione,8-acetyl-10-[(3-amino-2,3,6-trideoxy)-alpha-L-lyxo-hexopyranosyl)oxy]-7,8,9,10-tetrahydro-6,8,11-trihydroxy-1-methoxy-, (8S-cis)- Daunomycin 20830-81-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U181 99-55-8 5-Nitro-o-toluidine 5-Nitro-o-toluidine 99-55-8 0.32 28 U094 57-97-6 7,12-Dimethylbenz[a]anthracene 7,12-Dimethylbenz(a)anthracene 57-97-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U367 1563-38-8 7-Benzofuranol, 2,3-dihydro-2,2-dimethyl- Carbofuran phenol 1563-38-8 0.056 1.4 U394 30558-43-1 A2213 A2213 30558-43-1 BIODG; CARBN; CHOXD; CMBST or 0.042 CMBST or 1.4 U001 75-07-0 Acetaldehyde Acetaldehyde 75-07-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U034 75-87-6 Acetaldehyde, trichloro- Trichloroacetaldehyde (Chloral) 75-87-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U187 62-44-2 Acetamide, N-(4-ethoxyphenyl)- Phenacetin 62-44-2 0.081 16 U005 53-96-3 Acetamide, N-9H-fluoren-2-yl- 2-Acetylaminofluorene 53-96-3 0.059 140 U112 141-78-6 Acetic acid ethyl ester Ethyl acetate 141-78-6 0.34 33 See F027 93-76-5 Acetic acid, (2,4,5-trichlorophenoxy)- See F027 in Schedule 1 U240 94-75-7 Acetic acid, (2,4-dichlorophenoxy)-,salts & esters See 2,4-D, salts & esters U144 301-04-2 Acetic acid, lead(2+) salt Lead 7439-92-1 0.69 0.75 mg/L TCLP U214 563-68-8 Acetic acid, thallium(1+) salt Thallium (measured in aqueous wastes only) 7440-28-0 1.4 RTHRM; or STABL U002 67-64-1 Acetone Acetone 67-64-1 0.28 160 U003 75-05-8 Acetonitrile Acetonitrile 75-05-8 5.6 CMBST or 38 U004 98-86-2 Acetophenone Acetophenone 98-86-2 0.010 9.7 U006 75-36-5 Acetyl chloride Acetyl Chloride 75-36-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U007 79-06-1 Acrylamide Acrylamide 79-06-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U008 79-10-7 Acrylic acid Acrylic acid 79-10-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U009 107-13-1 Acrylonitrile Acrylonitrile 107-13-1 0.24 84 U096 80-15-9 alpha,alpha-Dimethylbenzylhydroperoxide alpha, alpha-Dimethyl benzyl hydroperoxide 80-15-9 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U167 134-32-7 alpha-Naphthylamine 1-Naphthylamine 134-32-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U011 61-82-5 Amitrole Amitrole 61-82-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U012 62-53-3 Aniline Aniline 62-53-3 0.81 14 U136 75-60-5 Arsinic acid, dimethyl- Arsenic 7440-38-2 1.4 5.0 mg/L TCLP U014 492-80-8 Auramine Auramine 492-80-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U015 115-02-6 Azaserine Azaserine 115-02-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U010 50-07-7 Azirino[2,3_3,4]pyrrolo[1,2-a]indole-4,7-dione,6-amino-8-[[(aminocarbonyl)oxy]methyl]-1,1a,2,8,8a,8b-hexahydro-8a-methoxy-5-methyl-, [1aS-(1aalpha,8beta,8aalpha,8balpha)]- Mitomycin C 50-07-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U280 101-27-9 Barban Barban 101-27-9 0.056 1.4 U278 22781-23-3 Bendiocarb Bendiocarb 22781-23-3 0.056 1.4 U364 22961-82-6 Bendiocarb phenol Bendiocarb phenol 22961-82-6 BIODG; CARBN; CHOXD; CMBST or 0.056 CMBST or 1.4 U271 17804-35-2 Benomyl Benomyl 17804-35-2 0.056 1.4 U018 56-55-3 Benz[a]anthracene Benz(a)anthracene 56-55-3 0.059 3.4 U094 57-97-6 Benz[a]anthracene, 7,12-dimethyl- 7,12-Dimethylbenz(a)anthracene 57-97-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U016 225-51-4 Benz[c]acridine Benz(c)acridine 225-51-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U157 56-49-5 Benz[j]aceanthrylene, 1,2-dihydro-3-methyl- 3-Methylcholanthrene 56-49-5 0.0055 15 U017 98-87-3 Benzal chloride Benzal chloride 98-87-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U192 23950-58-5 Benzamide,3,5-dichloro-N-(1,1-dimethyl-2-propynyl)- Pronamide 23950-58-5 0.093 1.5 U012 62-53-3 Benzenamine Aniline 62-53-3 0.81 14 U328 95-53-4 Benzenamine, 2-methyl- o-Toluidine 95-53-4 CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN. CMBST U222 636-21-5 Benzenamine, 2-methyl-, hydrochloride o-Toluidine hydrochloride 636-21-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U181 99-55-8 Benzenamine, 2-methyl-5-nitro- 5-Nitro-o-toluidine 99-55-8 0.32 28 U014 492-80-8 Benzenamine, 4,4-carbonimidoylbis[N,N-dimethyl- Auramine 492-80-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U158 101-14-4 Benzenamine, 4,4-methylenebis[2-chloro- 4,4'-Methylene bis(2-chloroaniline) 101-14-4 0.50 30 U049 3165-93-3 Benzenamine, 4-chloro-2-methyl-,hydrochloride 4-Chloro-o-toluidine hydrochloride 3165-93-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U353 106-49-0 Benzenamine, 4-methyl- p-Toluidine 106-49-0 CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN. CMBST U093 60-11-7 Benzenamine, N,N-dimethyl-4-(phenylazo)- p-Dimethylaminoazobenzene 60-11-7 0.13 CMBST U019 71-43-2 Benzene Benzene 71-43-2 0.14 10 U055 98-82-8 Benzene, (1-methylethyl)- Cumene 98-82-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U017 98-87-3 Benzene, (dichloromethyl)- Benzal chloride 98-87-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U023 98-07-7 Benzene, (trichloromethyl)- Benzotrichloride 98-07-7 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U247 72-43-5 Benzene, 1,1-(2,2,2-trichloroethylidene)bis[4- methoxy- Methoxychlor 72-43-5 0.25 0.18 U207 95-94-3 Benzene, 1,2,4,5-tetrachloro- 1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14 U070 95-50-1 Benzene, 1,2-dichloro- o-Dichlorobenzene 95-50-1 0.088 6.0 U234 99-35-4 Benzene, 1,3,5-trinitro- 1,3,5-Trinitrobenzene 99-35-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U071 541-73-1 Benzene, 1,3-dichloro- m-Dichlorobenzene 541-73-1 0.036 6.0 U223 26471-62-5 Benzene, 1,3-diisocyanatomethyl- Toluene diisocyanate 26471-62-5 CARBN; or CMBST CMBST U072 106-46-7 Benzene, 1,4-dichloro- p-Dichlorobenzene 106-46-7 0.09 6.0 U030 101-55-3 Benzene, 1-bromo-4-phenoxy- 4-Bromophenyl phenyl ether 101-55-3 0.055 15 U105 121-14-2 Benzene, 1-methyl-2,4-dinitro- 2,4-Dinitrotoluene 121-14-2 0.32 140 U106 606-20-2 Benzene, 2-methyl-1,3-dinitro- 2,6-Dinitrotoluene 606-20-2 0.55 28 U037 108-90-7 Benzene, chloro- Chlorobenzene 108-90-7 0.057 60 U239 1330-20-7 Benzene, dimethyl- Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 U127 118-74-1 Benzene, hexachloro- Hexachlorobenzene 118-74-1 0.055 10 U056 110-82-7 Benzene, hexahydro- Cyclohexane 110-82-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U220 108-88-3 Benzene, methyl- Toluene 108-88-3 0.08 10 U169 98-95-3 Benzene, nitro- Nitrobenzene 98-95-3 0.068 14 U183 608-93-5 Benzene, pentachloro- Pentachlorobenzene 608-93-5 0.055 10 U185 82-68-8 Benzene, pentachloronitro- Pentachloronitrobenzene 82-68-8 0.055 4.8 U061 50-29-3 Benzene,1,1-(2,2,2-trichloroethylidene)bis[4-chloro- o,p'-DDT 789-02-6 0.0039 0.087 p,p'-DDT 50-29-3 0.0039 0.087 o,p'-DDD 53-19-0 0.023 0.087 p,p'-DDD 72-54-8 0.023 0.087 o,p'-DDE 3424-82-6 0.031 0.087 p,p'-DDE 72-55-9 0.031 0.087 U060 72-54-8 Benzene,1,1-(2,2-dichloroethylidene)bis[4-chloro- o,p'-DDD 53-19-0 0.023 0.087 p,p'-DDD 72-54-8 0.023 0.087 U038 510-15-6 Benzeneacetic acid,4-chloro-alpha- (4-chlorophenyl)-alpha-hydroxy-, ethyl ester Chlorobenzilate 510-15-6 0.10 CMBST U035 305-03-3 Benzenebutanoic acid, 4-[bis(2-chloroethyl)amino]- Chlorambucil 305-03-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U221 25376-45-8 Benzenediamine, ar-methyl- Toluenediamine 25376-45-8 CARBN; or CMBST CMBST U020 98-09-9 Benzenesulfonic acid chloride Benzenesulfonyl chloride 98-09-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U020 98-09-9 Benzenesulfonyl chloride Benzenesulfonyl chloride 98-09-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U021 92-87-5 Benzidine Benzidine 92-87-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U022 50-32-8 Benzo[a]pyrene Benzo(a)pyrene 50-32-8 0.061 3.4 U064 189-55-9 Benzo[rst]pentaphene Dibenz(a,i)pyrene 189-55-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U023 98-07-7 Benzotrichloride Benzotrichloride 98-07-7 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U047 91-58-7 beta-Chloronaphthalene 2-Chloronaphthalene 91-58-7 0.055 5.6 U168 91-59-8 beta-Naphthylamine 2-Naphthylamine 91-59-8 0.52 CMBST U225 75-25-2 Bromoform Bromoform (Tribromomethane) 75-25-2 0.63 15 U136 75-60-5 Cacodylic acid Arsenic 7440-38-2 1.4 5.0 mg/L TCLP U032 13765-19-0 Calcium chromate Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP U280 101-27-9 Carbamic acid, (3-chlorophenyl)-, 4-chloro-2-butynyl ester Barban 101-27-9 0.056 1.4 U409 23564-05-8 Carbamic acid, [1,2-phenylenebis (iminocarbonothioyl)]bis-, dimethyl ester Thiophanate-methyl 23564-05-8 0.056 1.4 U271 17804-35-2 Carbamic acid, [1-[(butylamino)carbonyl]-1H-benzimidazol-2-yl]-, methyl ester Benomyl 17804-35-2 0.056 1.4 U372 10605-21-7 Carbamic acid, 1H-benzimidazol-2-yl,methyl ester Carbendazim 10605-21-7 0.056 1.4 U238 51-79-6 Carbamic acid, ethyl ester Urethane (Ethyl carbamate) 51-79-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U178 615-53-2 Carbamic acid, methylnitroso-, ethyl ester N-Nitroso-N-methylurethane 615-53-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U373 122-42-9 Carbamic acid, phenyl-, 1-methylethyl ester Propham 122-42-9 0.056 1.4 U097 79-44-7 Carbamic chloride, dimethyl- Dimethylcarbamoyl chloride 79-44-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U114 111-54-6 Carbamodithioic acid, 1,2-ethanediylbis-,salts & esters Ethylenebisdithiocarbamic acid 111-54-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U389 2303-17-5 Carbamothioic acid, bis(1-methylethyl)-, S-(2,3,3-trichloro-2-propenyl)ester Triallate 2303-17-5 0.042 1.4 U062 2303-16-4 Carbamothioic acid, bis(1-methylethyl)-S-(2,3-dichloro-2-propenyl) ester Diallate 2303-16-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U387 52888-80-9 Carbamothioic acid, dipropyl-, S-(phenylmethyl) ester Prosulfocarb 52888-80-9 0.042 1.4 U279 63-25-2 Carbaryl. Carbaryl 63-25-2 0.006 0.14 U372 10605-21-7 Carbendazim Carbendazim 10605-21-7 0.056 1.4 U367 1563-38-8 Carbofuran phenol Carbofuran phenol 1563-38-8 0.056 1.4 U033 353-50-4 Carbon oxyfluoride Carbon oxyfluoride 353-50-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U211 56-23-5 Carbon tetrachloride Carbon tetrachloride 56-23-5 0.057 6.0 U215 6533-73-9 Carbonic acid, dithallium(1+) salt Thallium (measured in aqueous wastes only) 7440-28-0 1.4 RTHRM; or STABL U033 353-50-4 Carbonic difluoride Carbon oxyfluoride 353-50-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U156 79-22-1 Carbonochloridic acid, methyl ester Methyl chlorocarbonate 79-22-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U034 75-87-6 Chloral Trichloroacetaldehyde (Chloral) 75-87-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U035 305-03-3 Chlorambucil Chlorambucil 305-03-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U036 57-74-9 Chlordane, alpha & gamma isomers Chlordane (alpha and gamma isomers) 57-74-9 0.0033 0.26 U026 494-03-1 Chlornaphazin Chlornaphazine 494-03-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U037 108-90-7 Chlorobenzene Chlorobenzene 108-90-7 0.057 60 U038 510-15-6 Chlorobenzilate Chlorobenzilate 510-15-6 0.10 CMBST U044 67-66-3 Chloroform Chloroform 67-66-3 0.046 6.0 U046 107-30-2 Chloromethyl methyl ether Chloromethyl methyl ether 107-30-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U032 13765-19-0 Chromic acid H2CrO4, calcium salt Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP U050 218-01-9 Chrysene Chrysene 218-01-9 0.059 3.4 U051 NA Creosote Naphthalene 91-20-3 0.059 5.6 Pentachlorophenol 87-86-5 0.089 7.4 Phenanthrene 85-01-8 0.059 5.6 Pyrene 129-00-0 0.067 8.2 Toluene 108-88-3 0.08 10 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 Lead 7439-92-1 0.69 0.75 mg/L TCLP U052 1319-77-3 Cresol (Cresylic acid) o-Cresol 95-48-7 0.11 5.6 m-Cresol (difficult to distinguish from p-cresol) 108-39-4 0.77 5.6 p-Cresol (difficult to distinguish from m-cresol) 106-44-5 0.77 5.6 Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations) 1319-77-3 0.88 11.2 U053 4170-30-3 Crotonaldehyde Crotonaldehyde 4170-30-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U055 98-82-8 Cumene Cumene 98-82-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U246 506-68-3 Cyanogen bromide (CN)Br Cyanogen bromide 506-68-3 CHOXD; WETOX; or CMBST CHOXD; WETOX; or CMBST U056 110-82-7 Cyclohexane Cyclohexane 110-82-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U129 58-89-9 Cyclohexane, 1,2,3,4,5,6-hexachloro-,(1alpha,2alpha,3beta,4alpha,5alpha,6 beta)- alpha-BHC 319-84-6 0.00014 0.066 beta-BHC 319-85-7 0.00014 0.066 delta-BHC 319-86-8 0.023 0.066 gamma-BHC (Lindane) 58-89-9 0.0017 0.066 U057 108-94-1 Cyclohexanone Cyclohexanone 108-94-1 0.36 CMBST or 0.75 mg/L TCLP U058 50-18-0 Cyclophosphamide Cyclophosphamide 50-18-0 CARBN; or CMBST CMBST U059 20830-81-3 Daunomycin Daunomycin 20830-81-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U060 72-54-8 DDD o,p'-DDD 53-19-0 0.023 0.087 p,p'-DDD 72-54-8 0.023 0.087 U061 50-29-3 DDT o,p'-DDT 789-02-6 0.0039 0.087 p,p'-DDT 50-29-3 0.0039 0.087 o,p'-DDD 53-19-0 0.023 0.087 p,p'-DDD 72-54-8 0.023 0.087 o,p'-DDE 3424-82-6 0.031 0.087 p,p'-DDE 72-55-9 0.031 0.087 U206 18883-66-4 D-Glucose,2-deoxy-2-[[(methylnitrosoamino)-carbonyl]amino]- Streptozotocin 18883-66-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U062 2303-16-4 Diallate Diallate 2303-16-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U063 53-70-3 Dibenz[a,h]anthracene Dibenz(a,h)anthracene 53-70-3 0.055 8.2 U064 189-55-9 Dibenzo[a,i]pyrene Dibenz(a,i)pyrene 189-55-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U069 84-74-2 Dibutyl phthalate Di-n-butyl phthalate 84-74-2 0.057 28 U075 75-71-8 Dichlorodifluoromethane Dichlorodifluoromethane 75-71-8 0.23 7.2 U025 111-44-4 Dichloroethyl ether bis(2-Chloroethyl)ether 111-44-4 0.033 6.0 U027 108-60-1 Dichloroisopropyl ether bis(2-Chloroisopropyl)ether 39638-32-9 0.055 7.2 U024 111-91-1 Dichloromethoxy ethane bis(2-Chloroethoxy)methane 111-91-1 0.036 7.2 U088 84-66-2 Diethyl phthalate Diethyl phthalate 84-66-2 0.20 28 U395 5952-26-1 Diethylene glycol, dicarbamate Diethylene glycol, dicarbamate 5952-26-1 BIODG; CARBN; CHOXD; CMBST or 0.056 CMBST or 1.4 U028 117-81-7 Diethylhexyl phthalate bis(2-Ethylhexyl) phthalate 117-81-7 0.28 28 U089 56-53-1 Diethyl stilbesterol Diethyl stilbestrol 56-53-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U090 94-58-6 Dihydrosafrole Dihydrosafrole 94-58-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U102 131-11-3 Dimethyl phthalate Dimethyl phthalate 131-11-3 0.047 28 U103 77-78-1 Dimethyl sulfate Dimethyl sulfate 77-78-1 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U092 124-40-3 Dimethylamine Dimethylamine 124-40-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U097 79-44-7 Dimethylcarbamoyl chloride Dimethylcarbamoyl chloride 79-44-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U107 117-84-0 Di-n-octyl phthalate Di-n-octyl phthalate 117-84-0 0.017 28 U111 621-64-7 Di-n-propylnitrosamine Di-n-propylnitrosamine 621-64-7 0.40 14 U110 142-84-7 Dipropylamine Dipropylamine 142-84-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U041 106-89-8 Epichlorohydrin Epichlorohydrin (1-Chloro-2,3-epoxypropane) 106-89-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U001 75-07-0 Ethanal Acetaldehyde 75-07-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U404 121-44-8 Ethanamine, N,N-diethyl- Triethylamine 121-44-8 0.081 1.5 U174 55-18-5 Ethanamine, N-ethyl-N-nitroso- N-Nitrosodiethylamine 55-18-5 0.40 28 U208 630-20-6 Ethane, 1,1,1,2-tetrachloro- 1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0 U226 71-55-6 Ethane, 1,1,1-trichloro- 1,1,1-Trichloroethane 71-55-6 0.054 6.0 U209 79-34-5 Ethane, 1,1,2,2-tetrachloro- 1,1,2,2-Tetrachloroethane 79-34-5 0.057 6.0 U227 79-00-5 Ethane, 1,1,2-trichloro- 1,1,2-Trichloroethane 79-00-5 0.054 6.0 U024 111-91-1 Ethane, 1,1'-[methylenebis(oxy)]bis[2-chloro- bis(2-Chloroethoxy)methane 111-91-1 0.036 7.2 U076 75-34-3 Ethane, 1,1-dichloro- 1,1-Dichloroethane 75-34-3 0.059 6.0 U117 60-29-7 Ethane, 1,1'-oxybis- Ethyl ether 60-29-7 0.12 160 U025 111-44-4 Ethane, 1,1'-oxybis[2-chloro- bis(2-Chloroethyl)ether 111-44-4 0.033 6.0 U067 106-93-4 Ethane, 1,2-dibromo- Ethylene dibromide (1,2-Dibromoethane) 106-93-4 0.028 15 U077 107-06-2 Ethane, 1,2-dichloro- 1,2-Dichloroethane 107-06-2 0.21 6.0 U131 67-72-1 Ethane, hexachloro- Hexachloroethane 67-72-1 0.055 30 U184 76-01-7 Ethane, pentachloro- Pentachloroethane 76-01-7 (WETOX or CHOXD) fb CARBN; or CMBST or 0.055 CMBST or 6.0 U218 62-55-5 Ethanethioamide Thioacetamide 62-55-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U394 30558-43-1 Ethanimidothioic acid, 2-(dimethylamino)-N-hydroxy-2-oxo-,methyl ester A2213 30558-43-1 BIODG; CARBN; CHOXD; CMBST or 0.042 CMBST or 1.4 U410 59669-26-0 Ethanimidothioic acid, N,N'-[thiobis[(methylimino)carbonyloxy]]bi s-, dimethyl ester Thiodicarb 59669-26-0 0.019 1.4 U173 1116-54-7 Ethanol, 2,2'-(nitrosoimino)bis- N-Nitrosodiethanolamine 1116-54-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U395 5952-26-1 Ethanol, 2,2'-oxybis-, dicarbamate Diethylene glycol, dicarbamate 5952-26-1 BIODG; CARBN; CHOXD; CMBST or 0.056 CMBST or 1.4 U359 110-80-5 Ethanol, 2-ethoxy- 2-Ethoxyethanol 110-80-5 CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN. CMBST U004 98-86-2 Ethanone, 1-phenyl- Acetophenone 98-86-2 0.010 9.7 U042 110-75-8 Ethene, (2-chloroethoxy)- 2-Chloroethyl vinyl ether 110-75-8 0.062 CMBST U078 75-35-4 Ethene, 1,1-dichloro- 1,1-Dichloroethylene 75-35-4 0.025 6.0 U079 156-60-5 Ethene, 1,2-dichloro-, (E)- trans-1,2-Dichloroethylene 156-60-5 0.054 30 U043 75-01-4 Ethene, chloro- Vinyl chloride 75-01-4 0.27 6.0 U210 127-18-4 Ethene, tetrachloro- Tetrachloroethylene 127-18-4 0.056 6.0 U228 79-01-6 Ethene, trichloro- Trichloroethylene 79-01-6 0.054 6.0 U112 141-78-6 Ethyl acetate Ethyl acetate 141-78-6 0.34 33 U113 140-88-5 Ethyl acrylate Ethyl acrylate 140-88-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U238 51-79-6 Ethyl carbamate (urethane) Urethane (Ethyl carbamate) 51-79-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U117 60-29-7 Ethyl ether Ethyl ether 60-29-7 0.12 160 U118 97-63-2 Ethyl methacrylate Ethyl methacrylate 97-63-2 0.14 160 U119 62-50-0 Ethyl methanesulfonate Ethyl methane sulfonate 62-50-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U067 106-93-4 Ethylene dibromide Ethylene dibromide (1,2-Dibromoethane) 106-93-4 0.028 15 U077 107-06-2 Ethylene dichloride 1,2-Dichloroethane 107-06-2 0.21 6.0 U359 110-80-5 Ethylene glycol monoethyl ether 2-Ethoxyethanol 110-80-5 CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN. CMBST U115 75-21-8 Ethylene oxide Ethylene oxide 75-21-8 (WETOX or CHOXD) fb CARBN; or CMBST or 0.12 CHOXD; or CMBST U114 111-54-6 Ethylenebisdithiocarbamic acid, salts & esters Ethylenebisdithiocarbamic acid 111-54-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U116 96-45-7 Ethylenethiourea Ethylene thiourea 96-45-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U076 75-34-3 Ethylidene dichloride 1,1-Dichloroethane 75-34-3 0.059 6.0 U120 206-44-0 Fluoranthene Fluoranthene 206-44-0 0.068 3.4 U122 50-00-0 Formaldehyde Formaldehyde 50-00-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U123 64-18-6 Formic acid Formic acid 64-18-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U124 110-00-9 Furan Furan 110-00-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U213 109-99-9 Furan, tetrahydro- Tetrahydrofuran 109-99-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U125 98-01-1 Furfural Furfural 98-01-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U124 110-00-9 Furfuran Furan 110-00-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U206 18883-66-4 Glucopyranose,2-deoxy-2-(3-methyl-3-nitrosoureido)-, D- Streptozotocin 18883-66-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U126 765-34-4 Glycidylaldehyde Glycidyaldehyde 765-34-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U163 70-25-7 Guanidine, N-methyl-N'-nitro-N-nitroso- N-Methyl N'-nitro N-nitrosoguanidine 70-25-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U127 118-74-1 Hexachlorobenzene Hexachlorobenzene 118-74-1 0.055 10 U128 87-68-3 Hexachlorobutadiene Hexachlorobutadiene 87-68-3 0.055 5.6 U130 77-47-4 Hexachlorocyclopentadiene Hexachlorocyclopentadiene 77-47-4 0.057 2.4 U131 67-72-1 Hexachloroethane Hexachloroethane 67-72-1 0.055 30 U132 70-30-4 Hexachlorophene Hexachlorophene 70-30-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U243 1888-71-7 Hexachloropropene Hexachloropropylene 1888-71-7 0.035 30 U133 302-01-2 Hydrazine Hydrazine 302-01-2 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U098 57-14-7 Hydrazine, 1,1-dimethyl- 1,1-Dimethylhydrazine 57-14-7 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U086 1615-80-1 Hydrazine, 1,2-diethyl- N,N'-Diethylhydrazine 1615-80-1 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U099 540-73-8 Hydrazine, 1,2-dimethyl- 1,2-Dimethylhydrazine 540-73-8 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U109 122-66-7 Hydrazine, 1,2-diphenyl- 1,2-Diphenylhydrazine 122-66-7 CHOXD; CHRED; CARBN; BIODG; CMBST or 0.087 CHOXD; CHRED; or CMBST U134 7664-39-3 Hydrofluoric acid Fluoride (measured in aqueous wastes only) 16984-48-8 35 ADGAS fb NEUTR; or NEUTR U134 7664-39-3 Hydrogen fluoride Fluoride (measured in aqueous wastes only) 16984-48-8 35 ADGAS fb NEUTR; or NEUTR U135 7783-06-4 Hydrogen sulfide Hydrogen Sulfide 7783-06-4 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST U135 7783-06-4 Hydrogen sulfide H2S Hydrogen Sulfide 7783-06-4 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST U096 80-15-9 Hydroperoxide, 1-methyl-1-phenylethyl- alpha, alpha-Dimethyl benzyl hydroperoxide 80-15-9 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U137 193-39-5 Indeno(1,2,3-cd)pyrene Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4 U140 78-83-1 Isobutyl alcohol Isobutyl alcohol 78-83-1 5.6 170 U141 120-58-1 Isosafrole Isosafrole 120-58-1 0.081 2.6 U142 143-50-0 Kepone Kepone 143-50-0 0.0011 0.13 U143 303-34-4 Lasiocarpine Lasiocarpine 303-34-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U144 301-04-2 Lead acetate Lead 7439-92-1 0.69 0.75 mg/L TCLP U145 7446-27-7 Lead phosphate Lead 7439-92-1 0.69 0.75 mg/L TCLP U146 1335-32-6 Lead subacetate Lead 7439-92-1 0.69 0.75 mg/L TCLP U146 1335-32-6 Lead, bis(acetato-O)tetrahydroxytri- Lead 7439-92-1 0.69 0.75 mg/L TCLP U129 58-89-9 Lindane alpha-BHC 319-84-6 0.00014 0.066 beta-BHC 319-85-7 0.00014 0.066 delta-BHC 319-86-8 0.023 0.066 gamma-BHC (Lindane) 58-89-9 0.0017 0.066 U150 148-82-3 L-Phenylalanine, 4-[bis(2-chloroethyl)amino]- Melphalan 148-82-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U015 115-02-6 L-Serine, diazoacetate (ester) Azaserine 115-02-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U147 108-31-6 Maleic anhydride Maleic anhydride 108-31-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U148 123-33-1 Maleic hydrazide Maleic hydrazide 123-33-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U149 109-77-3 Malononitrile Malononitrile 109-77-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U071 541-73-1 m-Dichlorobenzene m-Dichlorobenzene 541-73-1 0.036 6.0 U150 148-82-3 Melphalan Melphalan 148-82-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U151 7439-97-6 Mercury Treatment Subcategory 1 U151 (mercury) non-aqueous wastes that contain greater than or equal to 260 mg/ kg total mercury: Mercury 7439-97-6 NA RMERC Treatment Subcategory 2 U151 (mercury) non-aqueous wastes that contain less than 260 mg/kg total mercury and that are residues from RMERC only:

Mercury 7439-97-6 NA 0.20 mg/L TCLP Treatment Subcategory 3 U151 (mercury) non-aqueous wastes that contain less than 260 mg/kg total mercury and that are not residues from RMERC: Mercury 7439-97-6 NA 0.025 mg/L TCLP Treatment Subcategory 4 All U151 (mercury) aqueous wastes: Mercury 7439-97-6 0.15 NA Treatment Subcategory 5 Elemental Mercury Contaminated with Radioactive Materials: Mercury 7439-97-6 NA AMLGM U152 126-98-7 Methacrylonitrile Methacrylonitrile 126-98-7 0.24 84 U092 124-40-3 Methanamine, N-methyl- Dimethylamine 124-40-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U029 74-83-9 Methane, bromo- Methyl bromide (Bromomethane) 74-83-9 0.11 15 U045 74-87-3 Methane, chloro- Chloromethane (Methyl chloride) 74-87-3 0.19 30 U046 107-30-2 Methane, chloromethoxy- Chloromethyl methyl ether 107-30-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U068 74-95-3 Methane, dibromo- Dibromomethane 74-95-3 0.11 15 U080 75-09-2 Methane, dichloro- Methylene chloride 75-09-2 0.089 30 U075 75-71-8 Methane, dichlorodifluoro- Dichlorodifluoromethane 75-71-8 0.23 7.2 U138 74-88-4 Methane, iodo- Iodomethane 74-88-4 0.19 65 U211 56-23-5 Methane, tetrachloro- Carbon tetrachloride 56-23-5 0.057 6.0 U225 75-25-2 Methane, tribromo- Bromoform (Tribromomethane) 75-25-2 0.63 15 U044 67-66-3 Methane, trichloro- Chloroform 67-66-3 0.046 6.0 U121 75-69-4 Methane, trichlorofluoro- Trichlorofluoromethane 75-69-4 0.02 30 U119 62-50-0 Methanesulfonic acid, ethyl ester Ethyl methane sulfonate 62-50-0 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U153 74-93-1 Methanethiol Methanethiol 74-93-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U154 67-56-1 Methanol Methanol 67-56-1 (WETOX or CHOXD) fb CARBN; or CMBST or 5.6 CMBST or 0.75 mg/L TCLP U155 91-80-5 Methapyrilene Methapyrilene 91-80-5 0.081 1.5 U247 72-43-5 Methoxychlor Methoxychlor 72-43-5 0.25 0.18 U154 67-56-1 Methyl alcohol Methanol 67-56-1 (WETOX or CHOXD) fb CARBN; or CMBST or 5.6 CMBST or 0.75 mg/L TCLP U029 74-83-9 Methyl bromide Methyl bromide (Bromomethane) 74-83-9 0.11 15 U045 74-87-3 Methyl chloride Chloromethane (Methyl chloride) 74-87-3 0.19 30 U156 79-22-1 Methyl chlorocarbonate Methyl chlorocarbonate 79-22-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U226 71-55-6 Methyl chloroform 1,1,1-Trichloroethane 71-55-6 0.054 6.0 U159 78-93-3 Methyl ethyl ketone (MEK) Methyl ethyl ketone 78-93-3 0.28 36 U160 1338-23-4 Methyl ethyl ketone peroxide Methyl ethyl ketone peroxide 1338-23-4 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U138 74-88-4 Methyl iodide Iodomethane 74-88-4 0.19 65 U161 108-10-1 Methyl isobutyl ketone Methyl isobutyl ketone 108-10-1 0.14 33 U162 80-62-6 Methyl methacrylate Methyl methacrylate 80-62-6 0.14 160 U068 74-95-3 Methylene bromide Dibromomethane 74-95-3 0.11 15 U080 75-09-2 Methylene chloride Methylene chloride 75-09-2 0.089 30 U164 56-04-2 Methylthiouracil Methylthiouracil 56-04-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U010 50-07-7 Mitomycin C Mitomycin C 50-07-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U163 70-25-7 MNNG N-Methyl N'-nitro N-nitrosoguanidine 70-25-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U086 1615-80-1 N,N'-Diethylhydrazine N,N'-Diethylhydrazine 1615-80-1 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U026 494-03-1 Naphthalenamine, N,N'-bis(2-chloroethyl)- Chlornaphazine 494-03-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U165 91-20-3 Naphthalene Naphthalene 91-20-3 0.059 5.6 U047 91-58-7 Naphthalene, 2-chloro- 2-Chloronaphthalene 91-58-7 0.055 5.6 U031 71-36-3 n-Butyl alcohol n-Butyl alcohol 71-36-3 5.6 2.6 U217 10102-45-1 Nitric acid, thallium(1+) salt Thallium (measured in aqueous wastes only) 7440-28-0 1.4 RTHRM; or STABL U169 98-95-3 Nitrobenzene Nitrobenzene 98-95-3 0.068 14 U173 1116-54-7 N-Nitrosodiethanolamine N-Nitrosodiethanolamine 1116-54-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U174 55-18-5 N-Nitrosodiethylamine N-Nitrosodiethylamine 55-18-5 0.40 28 U172 924-16-3 N-Nitrosodi-n-butylamine N-Nitroso-di-n-butylamine 924-16-3 0.04 17 U176 759-73-9 N-Nitroso-N-ethylurea N-Nitroso-N-ethylurea 759-73-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U177 684-93-5 N-Nitroso-N-methylurea N-Nitroso-N-methylurea 684-93-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U178 615-53-2 N-Nitroso-N-methylurethane N-Nitroso-N-methylurethane 615-53-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U179 100-75-4 N-Nitrosopiperidine N-Nitrosopiperidine 100-75-4 0.013 35 U180 930-55-2 N-Nitrosopyrrolidine N-Nitrosopyrrolidine 930-55-2 0.013 35 U194 107-10-8 n-Propylamine n-Propylamine 107-10-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U087 3288-58-2 O,O-Diethyl S-methyl dithiophosphate O,O-Diethyl S-methyldithiophosphate 3288-58-2 CARBN; or CMBST CMBST U048 95-57-8 o-Chlorophenol 2-Chlorophenol 95-57-8 0.044 5.7 U070 95-50-1 o-Dichlorobenzene o-Dichlorobenzene 95-50-1 0.088 6.0 U328 95-53-4 o-Toluidine o-Toluidine 95-53-4 CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN. CMBST U222 636-21-5 o-Toluidine hydrochloride o-Toluidine hydrochloride 636-21-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U115 75-21-8 Oxirane Ethylene oxide 75-21-8 (WETOX or CHOXD) fb CARBN; or CMBST or 0.12 CHOXD; or CMBST U041 106-89-8 Oxirane, (chloromethyl)- Epichlorohydrin (1-Chloro-2,3-epoxypropane) 106-89-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U126 765-34-4 Oxiranecarboxyaldehyde Glycidyaldehyde 765-34-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U182 123-63-7 Paraldehyde Paraldehyde 123-63-7 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U197 106-51-4 p-Benzoquinone p-Benzoquinone 106-51-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U039 59-50-7 p-Chloro-m-cresol p-Chloro-m-cresol 59-50-7 0.018 14 U072 106-46-7 p-Dichlorobenzene p-Dichlorobenzene 106-46-7 0.09 6.0 U093 60-11-7 p-Dimethylaminoazobenzene p-Dimethylaminoazobenzene 60-11-7 0.13 CMBST U183 608-93-5 Pentachlorobenzene Pentachlorobenzene 608-93-5 0.055 10 U184 76-01-7 Pentachloroethane Pentachloroethane 76-01-7 (WETOX or CHOXD) fb CARBN; or CMBST or 0.055 CMBST or 6.0 U185 82-68-8 Pentachloronitrobenzene (PCNB) Pentachloronitrobenzene 82-68-8 0.055 4.8 See F027 87-86-5 Pentachlorophenol See F027 in Schedule 1 U161 108-10-1 Pentanol, 4-methyl- Methyl isobutyl ketone 108-10-1 0.14 33 U187 62-44-2 Phenacetin Phenacetin 62-44-2 0.081 16 U188 108-95-2 Phenol Phenol 108-95-2 0.039 6.2 U411 114-26-1 Phenol, 2-(1-methylethoxy)-,methylcarbamate Propoxur 114-26-1 0.056 1.4 See F027 58-90-2 Phenol, 2,3,4,6-tetrachloro- See F027 in Schedule 1 See F027 95-95-4 Phenol, 2,4,5-trichloro- See F027 in Schedule 1 See F027 88-06-2 Phenol, 2,4,6-trichloro- See F027 in Schedule 1 U081 120-83-2 Phenol, 2,4-dichloro- 2,4-Dichlorophenol 120-83-2 0.044 14 U101 105-67-9 Phenol, 2,4-dimethyl- 2,4-Dimethylphenol 105-67-9 0.036 14 U082 87-65-0 Phenol, 2,6-dichloro- 2,6-Dichlorophenol 87-65-0 0.044 14 U048 95-57-8 Phenol, 2-chloro- 2-Chlorophenol 95-57-8 0.044 5.7 U089 56-53-1 Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-, (E)- Diethyl stilbestrol 56-53-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U039 59-50-7 Phenol, 4-chloro-3-methyl- p-Chloro-m-cresol 59-50-7 0.018 14 U170 100-02-7 Phenol, 4-nitro- p-Nitrophenol 100-02-7 0.12 29 U052 1319-77-3 Phenol, methyl- o-Cresol 95-48-7 0.11 5.6 m-Cresol (difficult to distinguish from p-cresol) 108-39-4 0.77 5.6 p-Cresol (difficult to distinguish from m-cresol) 106-44-5 0.77 5.6 Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations) 1319-77-3 0.88 11.2 See F027 87-86-5 Phenol, pentachloro- See F027 in Schedule 1 U132 70-30-4 Phenol,2,2'-methylenebis[3,4,6-trichloro- Hexachlorophene 70-30-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U145 7446-27-7 Phosphoric acid, lead(2+) salt (2:3) Lead 7439-92-1 0.69 0.75 mg/L TCLP U087 3288-58-2 Phosphorodithioic acid, O,O-diethyl S-methyl ester O,O-Diethyl S-methyldithiophosphate 3288-58-2 CARBN; or CMBST CMBST U189 1314-80-3 Phosphorus sulfide Phosphorus sulfide 1314-80-3 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST U190 85-44-9 Phthalic anhydride Phthalic anhydride (measured as Phthalic acid or Terephthalic acid) 100-21-0; 85-44-9 0.055 28 U179 100-75-4 Piperidine, 1-nitroso- N-Nitrosopiperidine 100-75-4 0.013 35 U170 100-02-7 p-Nitrophenol p-Nitrophenol 100-02-7 0.12 29 U192 23950-58-5 Pronamide Pronamide 23950-58-5 0.093 1.5 U066 96-12-8 Propane, 1,2-dibromo-3-chloro- 1,2-Dibromo-3-chloropropane 96-12-8 0.11 15 U083 78-87-5 Propane, 1,2-dichloro- 1,2-Dichloropropane 78-87-5 0.85 18 U027 108-60-1 Propane, 2,2'-oxybis[2-chloro- bis(2-Chloroisopropyl)ether 39638-32-9 0.055 7.2 U171 79-46-9 Propane, 2-nitro- 2-Nitropropane 79-46-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U149 109-77-3 Propanedinitrile Malononitrile 109-77-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST See F027 93-72-1 Propanoic acid, 2-(2,4,5-0 trichlorophenoxy)- See F027 in Schedule 1 U373 122-42-9 Propham Propham 122-42-9 0.056 1.4 U411 114-26-1 Propoxur Propoxur 114-26-1 0.056 1.4 U083 78-87-5 Propylene dichloride 1,2-Dichloropropane 78-87-5 0.85 18 U387 52888-80-9 Prosulfocarb Prosulfocarb 52888-80-9 0.042 1.4 U353 106-49-0 p-Toluidine p-Toluidine 106-49-0 CMBST; or CHOXD fb (BIODG or CARBN); or BIODG fb CARBN. CMBST U196 110-86-1 Pyridine Pyridine 110-86-1 0.014 16 U191 109-06-8 Pyridine, 2-methyl- 2-Picoline 109-06-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U180 930-55-2 Pyrrolidine, 1-nitroso- N-Nitrosopyrrolidine 930-55-2 0.013 35 U200 50-55-5 Reserpine Reserpine 50-55-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U201 108-46-3 Resorcinol Resorcinol 108-46-3 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U202 81-07-2 Saccharin, & salts Saccharin 81-07-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U203 94-59-7 Safrole Safrole 94-59-7 0.081 22 U204 7783-00-8 Selenious acid Selenium 7782-49-2 0.82 5.7 mg/L TCLP U204 7783-00-8 Selenium dioxide Selenium 7782-49-2 0.82 5.7 mg/L TCLP U205 7488-56-4 Selenium sulfide Selenium 7782-49-2 0.82 5.7 mg/L TCLP U205 7488-56-4 Selenium sulfide SeS2 Selenium 7782-49-2 0.82 5.7 mg/L TCLP See F027 93-72-1 Silvex (2,4,5-TP) See F027 in Schedule 1 U206 18883-66-4 Streptozotocin Streptozotocin 18883-66-4 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U189 1314-80-3 Sulfur phosphide Phosphorus sulfide 1314-80-3 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST U103 77-78-1 Sulfuric acid, dimethyl ester Dimethyl sulfate 77-78-1 CHOXD; CHRED; CARBN; BIODG; or CMBST CHOXD; CHRED; or CMBST U210 127-18-4 Tetrachloroethylene Tetrachloroethylene 127-18-4 0.056 6.0 U213 109-99-9 Tetrahydrofuran Tetrahydrofuran 109-99-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U216 7791-12-0 Thallium chloride TlCl Thallium (measured in aqueous wastes only) 7440-28-0 1.4 RTHRM; or STABL U214 563-68-8 Thallium(I) acetate Thallium (measured in aqueous wastes only) 7440-28-0 1.4 RTHRM; or STABL U215 6533-73-9 Thallium(I) carbonate Thallium (measured in aqueous wastes only) 7440-28-0 1.4 RTHRM; or STABL U216 7791-12-0 Thallium(I) chloride Thallium (measured in aqueous wastes only) 7440-28-0 1.4 RTHRM; or STABL U217 10102-45-1 Thallium(I) nitrate Thallium (measured in aqueous wastes only) 7440-28-0 1.4 RTHRM; or STABL U218 62-55-5 Thioacetamide Thioacetamide 62-55-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U410 59669-26-0 Thiodicarb Thiodicarb 59669-26-0 0.019 1.4 U153 74-93-1 Thiomethanol Methanethiol 74-93-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U244 137-26-8 Thioperoxydicarbonic diamide[(H2N)C(S)]2S2, tetramethyl- Thiram 137-26-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U409 23564-05-8 Thiophanate-methyl Thiophanate-methyl 23564-05-8 0.056 1.4 U219 62-56-6 Thiourea Thiourea 62-56-6 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U244 137-26-8 Thiram Thiram 137-26-8 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U220 108-88-3 Toluene Toluene 108-88-3 0.08 10 U223 26471-62-5 Toluene diisocyanate Toluene diisocyanate 26471-62-5 CARBN; or CMBST CMBST U221 25376-45-8 Toluenediamine Toluenediamine 25376-45-8 CARBN; or CMBST CMBST U389 2303-17-5 Triallate Triallate 2303-17-5 0.042 1.4 U228 79-01-6 Trichloroethylene Trichloroethylene 79-01-6 0.054 6.0 U121 75-69-4 Trichloromonofluoromethane Trichlorofluoromethane 75-69-4 0.02 30 U404 121-44-8 Triethylamine Triethylamine 121-44-8 0.081 1.5 U235 126-72-7 Tris(2,3-Dibromopropyl) phosphate Tris(2,3-Dibromopropyl) phosphate 126-72-7 0.11 0.10 U236 72-57-1 Trypan blue Trypan Blue 72-57-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U237 66-75-1 Uracil mustard Uracil mustard 66-75-1 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U176 759-73-9 Urea, N-ethyl-N-nitroso- N-Nitroso-N-ethylurea 759-73-9 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U177 684-93-5 Urea, N-methyl-N-nitroso- N-Nitroso-N-methylurea 684-93-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U043 75-01-4 Vinyl chloride Vinyl chloride 75-01-4 0.27 6.0 U248 81-81-2 Warfarin, & salts, when present at concentrations of 0.3% or less Warfarin 81-81-2 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U239 1330-20-7 Xylene Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 U200 50-55-5 Yohimban-16-carboxylic acid,11,17-dimethoxy-18-[(3,4,5-trimethoxybenzoyl)oxy]-methyl ester,(3beta,16beta,17alpha, 18beta,20alpha)- Reserpine 50-55-5 (WETOX or CHOXD) fb CARBN; or CMBST CMBST U249 1314-84-7 Zinc phosphide Zn3P2, when present at concentrations of 10% or less Zinc Phosphide 1314-84-7 CHOXD; CHRED; or CMBST CHOXD; CHRED; or CMBST Notes to Part B of Schedule 2: 1 Treatment subcategories are shown for some wastes. In these cases, it is necessary to identify the treatment subcategory that most closely describes the particular waste for which treatment is required. The land disposal treatment requirements for that waste are those shown for that treatment subcategory. 2 Haz. Waste Number means Hazardous Waste Number. These numbers are consistent with United States Environmental Protection Agency Hazardous Waste Numbers. If there is no United States Environmental Protection Agency Hazardous Waste Number for a waste, the Hazardous Waste Number is assigned to the waste by the Ontario Ministry of the Environment. 3 CAS Number means the Chemical Abstracts Service Registry Number. When the waste or a regulated constituent is described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only. 4 See Schedule 7 for a description of the treatment methods and treatment standards associated with each treatment code. In some cases, the entries in this Schedule may set out more than one treatment code for a regulated constituent. An entry may permit a choice of treatment methods. For example, the entry “CHOXD; BIODG; or CMBST” means that the waste may be treated using any of the treatment methods that are set out for those treatment codes in Schedule 7. An entry may require treatment methods to be applied in a particular sequence. For this purpose, the abbreviation “fb” means “followed by”. For example, the entry “CHOXD fb CARBN” means that the waste must first be treated using the treatment method that is set out for CHOXD in Schedule 7 and, following that treatment, it must be treated using the treatment method that is set out for CARBN in Schedule 7. An entry may combine a choice of treatment methods and a requirement to apply treatment methods in a particular sequence (for example, “(WETOX or CHOXD) fb CARBN; or CMBST”). 5 Concentration requirements for aqueous wastes are based on analysis of composite samples. 6 Concentration requirements for non-aqueous wastes are based on analysis of grab samples. O. Reg. 337/09, s. 21; O. Reg. 297/17, s. 3. Schedule 2.1 Exempt Acute Hazardous Waste Chemicals There are no wastes currently listed in this Schedule. O. Reg. 460/99, s. 8; O. Reg. 297/17, s. 4. Schedule 2.2 Exempt Hazardous Waste Chemicals There are no wastes currently listed in this Schedule. O. Reg. 460/99, s. 8; O. Reg. 297/17, s. 5. Schedule 3 Severely Toxic Contaminants This Schedule consists of a Table and Notes. Table Column 1 Severely Toxic Contaminant: Hazardous Waste Number Column 2 Severely Toxic Contaminant: CAS Number Column 3 Severely Toxic Contaminant Column 4 Regulated Constituent: Generic Name or other description Column 5 Regulated Constituent: CAS Number Column 6 Land Disposal Treatment Requirements for Aqueous Waste: Concentration (mg/L) Column 7 Land Disposal Treatment Requirements for Non-aqueous Waste: Concentration (mg/kg) S001 1402-68-2 Aflatoxin Aflatoxin 1402-68-2 NA NA S002 1746-01-6 2,3,7,8-Tetrachlorodibenzo-p-dioxin TCDDs (All Tetrachlorodibenzo-p-dioxins) 41903-57-5 0.000063 0.001 S003 40321-76-4 1,2,3,7,8-Pentachlorodibenzo-p-dioxin PeCDDs (All Pentachlorodibenzo-p-dioxins) 36088-22-9 0.000063 0.001 S004 39227-28-6 1,2,3,4,7,8-Hexachlorodibenzo-p-dioxin HxCDDs (All Hexachlorodibenzo-p-dioxins) 34465-46-8 0.000063 0.001 S005 57653-85-7 1,2,3,6,7,8-Hexachlorodibenzo-p-dioxin HxCDDs (All Hexachlorodibenzo-p-dioxins) 34465-46-8 0.000063 0.001 S006 19408-74-3 1,2,3,7,8,9-Hexachlorodibenzo-p-dioxin HxCDDs (All Hexachlorodibenzo-p-dioxins) 34465-46-8 0.000063 0.001 S007 51207-31-9 2,3,7,8-Tetrachlorodibenzo furan TCDFs (All Tetrachlorodibenzofurans) 55722-27-5 0.000063 0.001 Notes to Schedule 3: 1. The Hazardous Waste Numbers are consistent with United States Environmental Protection Agency Hazardous Waste Numbers. If there is no United States Environmental Protection Agency Hazardous Waste Number for a waste, the Hazardous Waste Number is assigned to the waste by the Ontario Ministry of the Environment. 2. CAS Number means the Chemical Abstracts Service Registry Number. When the waste or a regulated constituent is described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only. 3. Concentration requirements for aqueous wastes are based on analysis of composite samples. 4. Concentration requirements for non-aqueous wastes are based on analysis of grab samples. O. Reg. 297/17, s. 6. Schedule 4 Leachate Quality Criteria This Schedule consists of a Table and Notes. Table Contaminant CAS Number Hazardous Waste Number Concentration (mg/L TCLP) Aldicarb 116-06-3 E101 0.9 Aldrin + Dieldrin 309-00-2, 60-57-1 E001 0.07 Arsenic 7440-38-2 D004 2.5 Atrazine + N-dealkylated metabolites (Weedex) 1912-24-9 E102 0.5 Azinphos-methyl 86-50-0 E103 2 Barium 7440-39-3 D005 100 Bendiocarb 22781-23-3 E002 4 Benzene 71-43-2 D018 0.5 Benzo(a)pyrene 50-32-8 E003 0.001 Boron 7440-42-8 E104 500 Bromoxynil 1689-84-5 E105 0.5 Cadmium 7440-43-9 D006 0.5 Carbaryl/Sevin/1-Naphthyl-N methyl carbamate 63-25-2 E004 9 Carbofuran 1563-66-2 E005 9 Carbon tetrachloride (Tetrachloromethane) 56-23-5 D019 0.5 Chlordane 57-74-9 D020 0.7 Chlorobenzene (Monochlorobenzene) 108-90-7 D021 8 Chloroform 67-66-3 D022 10 Chlorpyrifos 2921-88-2 E106 9 Chromium 7440-47-3 D007 5 Cresol (Mixture - total of all isomers, when isomers cannot be differentiated) NA D026 200 m-Cresol 108-39-4 D024 200 o-Cresol 95-48-7 D023 200 p-Cresol 106-44-5 D025 200 Cyanazine 21725-46-2 E107 1 Cyanide NA E006 20 2,4-D / (2,4-dichlorophenoxy)acetic acid 94-75-7 D016 10 2,4-DCP (2,4-Dichlorophenol) 120-83-2 E007 90 DDT (total isomers) NA E008 3 Diazinon/Phosphordithioic acid, o,o-diethyl o-(2-isopropyl 6-methyl-4-pyrimidinyl) ester 333-41-5 E108 2 Dicamba 1918-00-9 E109 12 1,2-Dichlorobenzene (o-Dichlorobenzene) 95-50-1 E009 20 1,4-Dichlorobenzene (p-Dichlorobenzene) 106-46-7 D027 0.5 1,2-Dichloroethane (Ethylene dichloride) 107-06-2 D028 0.5 1,1-Dichloroethylene (Vinylidene chloride) 75-35-4 D029 1.4 Dichloromethane (also see - methylene chloride) 75-09-02 E010 5 Diclofop-methyl 51338-27-3 E110 0.9 Dimethoate 60-51-5 E111 2 2,4-Dinitrotoluene 121-14-2 D030 0.13 Dinoseb 88-85-7 E012 1 Dioxin & Furan NA E013 0.0000015 Toxic Equivalent (TEQ) Diquat 231-36-7 E112 7 Diuron 330-54-1 E113 15 Endrin 72-20-8 D012 0.02 Fluoride NA E014 150 Glyphosate 1071-83-6 E114 28 Heptachlor + Heptachlor epoxide 76-44-8, 1024-57-3 D031 0.3 Hexachlorobenzene 118-74-1 D032 0.13 Hexachlorobutadiene 87-68-3 D033 0.5 Hexachloroethane 67-72-1 D034 3 Lead 7439-92-1 D008 5 Lindane 58-89-9 D013 0.4 Malathion 121-75-5 E115 19 Mercury 7439-97-6 D009 0.1 Methoxychlor/1,1,1-Trichloro-2,2-bis(p-methoxyphenyl) ethane 72-43-5 D014 90 Methyl ethyl ketone / Ethyl methyl ketone 78-93-3 D035 200 Methyl Parathion 298-00-0 E015 0.7 Methylene chloride / Dichloromethane 75-09-02 E011 5 Metolachlor 51218-45-2 E116 5 Metribuzin 21087-64-9 E117 8 NDMA 62-75-9 E016 0.0009 Nitrate + Nitrite (as Nitrogen) NA E118 1000 Nitrilotriacetic acid (NTA) 139-13-9 E119 40 Nitrobenzene 98-95-3 D036 2 Paraquat 4685-14-7 E120 1 Parathion 56-38-2 E017 5 PCBs NA E018 0.3 Pentachlorophenol 87-86-5 D037 6 Phorate 298-02-2 E019 0.2 Picloram 1918-02-1 E121 19 Pyridine 110-86-1 D038 5 Selenium 7782-49-2 D010 1 Silver 7440-22-4 D011 5 Simazine 122-34-9 E122 1 2,4,5-T (2,4,5-Trichlorophenoxyacetic acid) 93-76-5 E020 28 2,4,5-TP/ Silvex/ 2-(2,4,5-Trichlorophenoxy)propionic acid 93-72-1 D017 1 Temephos 3383-96-8 E123 28 Terbufos 13071-79-9 E124 0.1 Tetrachloroethylene 127-18-4 D039 3 2,3,4,6-Tetrachlorophenol /(2,3,4,6-TeCP) 58-90-2 E021 10 Toxaphene 8001-35-2 D015 0.5 Triallate 2303-17-5 E022 23 Trichloroethylene 79-01-6 D040 5 2,4,5-Trichlorophenol (2,4,5-TCP) 95-95-4 D041 400 2,4,6-Trichlorophenol (2,4,6-TCP) 88-06-2 D042 0.5 Trifluralin 1582-09-8 E125 4.5 Uranium 7440-61-1 E126 10 Vinyl chloride 75-01-4 D043 0.2 Notes to Schedule 4: 1. CAS Number means the Chemical Abstracts Service Registry Number. When the waste or a regulated constituent is described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only. 2. Hazardous Waste Numbers are consistent with United States Environmental Protection Agency Hazardous Waste Numbers. If there is no United States Environmental Protection Agency Hazardous Waste Number for a waste, the Hazardous Waste Number is assigned to the waste by the Ontario Ministry of the Environment. O. Reg. 297/17, s. 7. Schedule 5 Land Disposal TREATMENT Requirements FOR CHARACTERISTIC WASTES Characteristic Waste Regulated Constituents (and Treatment Subcategories1) Land Disposal Treatment Requirements Aqueous Waste Non-aqueous Waste Column 1 Haz. Waste Number2 Column 2 Waste Column 3 Generic Name or other description Column 4 CAS Number3 Column 5 Treatment Code4 or Concentration5 (mg/L) Column 6 Treatment Code4 or Concentration6 (mg/kg, unless otherwise indicated) D001 Ignitable Characteristic Wastes. Treatment Subcategory 1 Ignitable Characteristic Wastes, except for High TOC Ignitable Characteristic Liquids Subcategory. Ignitable Characteristic Wastes, except for wastes meeting (a) of the definition of ignitable waste AND greater than or equal to 10 per cent total organic carbon. NA DEACT and meet Schedule 6 standards; or RORGS; or CMBST DEACT and meet Schedule 6 standards; or RORGS; or CMBST Treatment Subcategory 2 High TOC Ignitable Characteristic Liquids. (Note: This subcategory consists of non-aqueous wastes only.) High TOC Ignitable Characteristic Liquids Subcategory based on (a) of definition of ignitable waste containing greater than or equal to 10 per cent total organic carbon. NA NA RORGS; CMBST; or POLYM D002 Corrosive Characteristic Wastes. Corrosive Characteristic Wastes. NA DEACT and meet Schedule 6 standards DEACT and meet Schedule 6 standards D003 Reactive Characteristic Wastes. Treatment Subcategory 1 Reactive Sulphides Subcategory Reactive Sulphides Subcategory based on (e) of the definition of reactive waste NA DEACT DEACT Treatment Subcategory 2 Explosives Subcategory Explosives Subcategory based on (f)(g)(h) of the definition of reactive waste NA DEACT and meet Schedule 6 standards DEACT and meet Schedule 6 standards Treatment Subcategory 3 Unexploded ordnance and other explosive devices which have been the subject of an emergency response. Unexploded ordnance and other explosive devices which have been the subject of an emergency response. NA DEACT DEACT Treatment Subcategory 4 Other Reactives Subcategory Other Reactives Subcategory based on (a) of the definition of reactive waste NA DEACT and meet Schedule 6 standards DEACT and meet Schedule 6 standards Treatment Subcategory 5 Water Reactive Subcategory Water Reactive Subcategory based on (b)(c)(d) of the definition of reactive waste. (Note: This subcategory consists of non-aqueous wastes only.) NA NA DEACT and meet Schedule 6 standards Treatment Subcategory 6 Reactive Cyanides Subcategory based on (e) of the definition of reactive waste. Cyanides (Total)7 57-12-5 NA 590 Cyanides (Amenable)7 57-12-5 0.86 30 D004 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for arsenic based on the Toxicity Characteristic Leaching Procedure. Arsenic 7440-38-2 1.4 and meet Schedule 6 standards 5.0 mg/L TCLP and meet Schedule 6 standards D005 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for barium based on the Toxicity Characteristic Leaching Procedure. Barium 7440-39-3 1.2 and meet Schedule 6 standards 21 mg/L TCLP and meet Schedule 6 standards D006 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for cadmium based on the Toxicity Characteristic Leaching Procedure. Treatment Subcategory 1 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for cadmium other than wastes in Treatment Subcategories 2 and 3. Cadmium 7440-43-9 0.69 and meet Schedule 6 standards 0.11 mg/L TCLP and meet Schedule 6 standards Treatment Subcategory 2 Cadmium containing batteries Subcategory other than wastes in Treatment Subcategory 3. (Note: This subcategory consists of non-aqueous wastes only.) Cadmium 7440-43-9 NA RTHRM Treatment Subcategory 3 Radioactively contaminated cadmium containing batteries. (Note: This subcategory consists of non-aqueous wastes only.) Cadmium 7440-43-9 NA Macroencapsulation in accordance with Schedule 8 (Alternative Treatment for Hazardous Debris) D007 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for chromium based on the Toxicity Characteristic Leaching Procedure. Chromium (Total) 7440-47-3 2.77 and meet Schedule 6 standards 0.60 mg/L TCLP and meet Schedule 6 standards D008 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for lead based on the Toxicity Characteristic Leaching Procedure. Treatment Subcategory 1 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for lead other than wastes in Treatment Subcategories 2 and 3. Lead 7439-92-1 0.69 and meet Schedule 6 standards 0.75 mg/L TCLP and meet Schedule 6 standards Treatment Subcategory 2 Lead acid batteries Subcategory. (Note: This standard only applies to lead acid batteries that are identified as hazardous wastes and that are not excluded elsewhere from regulation under Regulation 347 or through an environmental compliance approval [e.g. recycling].) Lead 7439-92-1 NA RLEAD Treatment Subcategory 3 Radioactive Lead Solids Subcategory. (Note: These lead solids include, but are not limited to, all forms of lead shielding and other elemental forms of lead. These lead solids do not include treatment residuals such as hydroxide sludges, other wastewater treatment residuals, or incinerator ashes that can undergo conventional pozzolanic stabilization, nor do they include organo-lead materials that can be incinerated and stabilized as ash. This subcategory consists of non-aqueous wastes only.) Lead 7439-92-1 NA MACRO D009 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury based on the Toxicity Characteristic Leaching Procedure. Treatment Subcategory 1 (High Mercury-Organic Subcategory) Non-aqueous wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury; and contain greater than or equal to 260 mg/kg total mercury that also contain organics and are not incinerator residues. Mercury 7439-97-6 NA IMERC; OR RMERC Treatment Subcategory 2 (High Mercury-Inorganic Subcategory) Non-aqueous wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury; and contain greater than or equal to 260 mg/kg total mercury that are inorganic, including incinerator residues and residues from RMERC. Mercury 7439-97-6 NA RMERC Treatment Subcategory 3 (Low Mercury Subcategory) Non-aqueous wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury; and contain less than 260 mg/kg total mercury and that are residues from RMERC only. Mercury 7439-97-6 NA 0.20 mg/L TCLP and meet Schedule 6 standards Treatment Subcategory 4 (Low Mercury Subcategory) All other non-aqueous wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for mercury; and contain less than 260 mg/kg total mercury and that are not residues from RMERC. Mercury 7439-97-6 NA 0.025 mg/L TCLP and meet Schedule 6 standards Treatment Subcategory 5 All aqueous wastes that exhibit or are expected to exhibit the characteristic of toxicity for mercury. Mercury 7439-97-6 0.15 mg/L TCLP and meet Schedule 6 standards NA Treatment Subcategory 6 (Mercury Radioactive Materials Subcategory) Elemental mercury contaminated with radioactive materials. (Note: This subcategory consists of non-aqueous wastes only.) Mercury 7439-97-6 NA AMLGM Treatment Subcategory 7 Hydraulic oil contaminated with Mercury Radioactive Materials Subcategory. (Note: This subcategory consists of non-aqueous wastes only.) Mercury 7439-97-6 NA IMERC Treatment Subcategory 8 Radioactively contaminated mercury containing batteries. (Note: This subcategory consists non-aqueous wastes only.) Mercury 7439-97-6 NA Macroencapsulation in accordance with Schedule 8 (Alternative Treatment for Hazardous Debris) D010 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for selenium based on the Toxicity Characteristic Leaching Procedure. Selenium 7782-49-2 0.82 and meet Schedule 6 standards 5.7 mg/L TCLP and meet Schedule 6 standards D011 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for silver based on the Toxicity Characteristic Leaching Procedure. Treatment Subcategory 1 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for silver other than wastes in Treatment Subcategory 2. Silver 7440-22-4 0.43 and meet Schedule 6 standards 0.14 mg/L TCLP and meet Schedule 6 standards Treatment Subcategory 2 Radioactively contaminated silver containing batteries Subcategory. (Note: This subcategory consists of non-aqueous wastes only.) Silver 7440-22-4 NA Macroencapsulation in accordance with Schedule 8 (Alternative Treatment for Hazardous Debris) D012 Wastes that are leachate toxic for Endrin based on the Toxicity Characteristic Leaching Procedure. Endrin 72-20-8 BIODG; or CMBST 0.13 and meet Schedule 6 standards Endrin aldehyde 7421-93-4 BIODG; or CMBST 0.13 and meet Schedule 6 standards D013 Wastes that are leachate toxic for Lindane based on the Toxicity Characteristic Leaching Procedure. alpha-BHC 319-84-6 CARBN; or CMBST 0.066 and meet Schedule 6 standards beta-BHC 319-85-7 CARBN; or CMBST 0.066 and meet Schedule 6 standards delta-BHC 319-86-8 CARBN; or CMBST 0.066 and meet Schedule 6 standards gamma-BHC (Lindane) 58-89-9 CARBN; or CMBST 0.066 and meet Schedule 6 standards D014 Wastes that are leachate toxic for Methoxychlor based on the Toxicity Characteristic Leaching Procedure. Methoxychlor 72-43-5 WETOX; or CMBST 0.18 and meet Schedule 6 standards D015 Wastes that are leachate toxic for Toxaphene based on the Toxicity Characteristic Leaching Procedure. Toxaphene 8001-35-2 BIODG; or CMBST 2.6 and meet Schedule 6 standards D016 Wastes that are leachate toxic for 2,4-D (2,4-Dichlorophenoxyacetic acid) based on the Toxicity Characteristic Leaching Procedure. 2,4,-D (2,4-Dichlorophenoxyacetic acid) 94-75-7 CHOXD; BIODG; or CMBST 10 and meet Schedule 6 standards D017 Wastes that are leachate toxic for 2,4,5-TP (Silvex) based on the Toxicity Characteristic Leaching Procedure. 2,4,5-TP (Silvex) 93-72-1 CHOXD; or CMBST 7.9 and meet Schedule 6 standards D018 Wastes that are leachate toxic for Benzene based on the Toxicity Characteristic Leaching Procedure. Benzene 71-43-2 0.14 and meet Schedule 6 standards 10 and meet Schedule 6 standards D019 Wastes that are leachate toxic for Carbon tetrachloride based on the Toxicity Characteristic Leaching Procedure. Carbon tetrachloride 56-23-5 0.057 and meet Schedule 6 standards 6.0 and meet Schedule 6 standards D020 Wastes that are leachate toxic for Chlordane based on the Toxicity Characteristic Leaching Procedure. Chlordane (alpha and gamma isomers) 57-74-9 0.0033 and meet Schedule 6 standards 0.26 and meet Schedule 6 standards D021 Wastes that are leachate toxic for Chlorobenzene based on the Toxicity Characteristic Leaching Procedure. Chlorobenzene 108-90-7 0.057 and meet Schedule 6 standards 6.0 and meet Schedule 6 standards D022 Wastes that are leachate toxic for Chloroform based on the Toxicity Characteristic Leaching Procedure. Chloroform 67-66-3 0.046 and meet Schedule 6 standards 6.0 and meet Schedule 6 standards D023 Wastes that are leachate toxic for o-Cresol based on the Toxicity Characteristic Leaching Procedure. o-Cresol 95-48-7 0.11 and meet Schedule 6 standards 5.6 and meet Schedule 6 standards D024 Wastes that are leachate toxic for m-Cresol based on the Toxicity Characteristic Leaching Procedure. m-Cresol (difficult to distinguish from p-cresol) 108-39-4 0.77 and meet Schedule 6 standards 5.6 and meet Schedule 6 standards D025 Wastes that are leachate toxic for p-Cresol based on the Toxicity Characteristic Leaching Procedure. p-Cresol (difficult to distinguish from m-cresol) 106-44-5 0.77 and meet Schedule 6 standards 5.6 and meet Schedule 6 standards D026 Wastes that are leachate toxic for Cresols (Total) based on the Toxicity Characteristic Leaching Procedure. Cresol-mixed isomers (Cresylic acid) (sum of o-, m-, and p-cresol concentrations) 1319-77-3 0.88 and meet Schedule 6 standards 11.2 and meet Schedule 6 standards D027 Wastes that are leachate toxic for p-Dichlorobenzene based on the Toxicity Characteristic Leaching Procedure. p-Dichlorobenzene (1,4-Dichlorobenzene) 106-46-7 0.090 and meet Schedule 6 standards 6.0 and meet Schedule 6 standards D028 Wastes that are leachate toxic for 1,2-Dichloroethane based on the Toxicity Characteristic Leaching Procedure. 1,2-Dichloroethane 107-06-2 0.21 and meet Schedule 6 standards 6.0 and meet Schedule 6 standards D029 Wastes that are leachate toxic for 1,1-Dichloroethylene based on the Toxicity Characteristic Leaching Procedure. 1,1-Dichloroethylene 75-35-4 0.25 and meet Schedule 6 standards 6.0 and meet Schedule 6 standards D030 Wastes that are leachate toxic for 2,4-Dinitrotoluene based on the Toxicity Characteristic Leaching Procedure. 2,4-Dinitrotoluene 121-14-2 0.32 and meet Schedule 6 standards 140 and meet Schedule 6 standards D031 Wastes that are leachate toxic for Heptachlor based on the Toxicity Characteristic Leaching Procedure. Heptachlor 76-44-8 0.0012 and meet Schedule 6 standards 0.066 and meet Schedule 6 standards Heptachlor epoxide 1024-57-3 0.016 and meet Schedule 6 standards 0.066 and meet Schedule 6 standards D032 Wastes that are leachate toxic for Hexachlorobenzene based on the Toxicity Characteristic Leaching Procedure. Hexachlorobenzene 118-74-1 0.055 and meet Schedule 6 standards 10 and meet Schedule 6 standards D033 Wastes that are leachate toxic for Hexachlorobutadiene based on the Toxicity Characteristic Leaching Procedure. Hexachlorobutadiene 87-68-3 0.055 and meet Schedule 6 standards 5.6 and meet Schedule 6 standards D034 Wastes that are leachate toxic for Hexachloroethane based on the Toxicity Characteristic Leaching Procedure. Hexachloroethane 67-72-1 0.055 and meet Schedule 6 standards 30 and meet Schedule 6 standards D035 Wastes that are leachate toxic for Methyl ethyl ketone based on the Toxicity Characteristic Leaching Procedure. Methyl ethyl ketone 78-93-3 0.28 and meet Schedule 6 standards 36 and meet Schedule 6 standards D036 Wastes that are leachate toxic for Nitrobenzene based on the Toxicity Characteristic Leaching Procedure. Nitrobenzene 98-95-3 0.068 and meet Schedule 6 standards 14 and meet Schedule 6 standards D037 Wastes that are leachate toxic for Pentachlorophenol based on the Toxicity Characteristic Leaching Procedure. Pentachlorophenol 87-86-5 0.089 and meet Schedule 6 standards 7.4 and meet Schedule 6 standards D038 Wastes that are leachate toxic for Pyridine based on the Toxicity Characteristic Leaching Procedure. Pyridine 110-86-1 0.014 and meet Schedule 6 standards 16 and meet Schedule 6 standards D039 Wastes that are leachate toxic for Tetrachloroethylene based on the Toxicity Characteristic Leaching Procedure. Tetrachloroethylene 127-18-4 0.056 and meet Schedule 6 standards 6.0 and meet Schedule 6 standards D040 Wastes that are leachate toxic for Trichloroethylene based on the Toxicity Characteristic Leaching Procedure. Trichloroethylene 79-01-6 0.054 and meet Schedule 6 standards 6.0 and meet Schedule 6 standards D041 Wastes that are leachate toxic for 2,4,5-Trichlorophenol based on the Toxicity Characteristic Leaching Procedure. 2,4,5-Trichlorophenol 95-95-4 0.18 and meet Schedule 6 standards 7.4 and meet Schedule 6 standards D042 Wastes that are leachate toxic for 2,4,6-Trichlorophenol based on the Toxicity Characteristic Leaching Procedure. 2,4,6-Trichlorophenol 88-06-2 0.035 and meet Schedule 6 standards 7.4 and meet Schedule 6 standards D043 Wastes that are leachate toxic for Vinyl chloride based on the Toxicity Characteristic Leaching Procedure. Vinyl chloride 75-01-4 0.27 and meet Schedule 6 standards 6.0 and meet Schedule 6 standards E001 Wastes that are leachate toxic for Aldrin + Dieldrin based on the Toxicity Characteristic Leaching Procedure. Aldrin 309-00-2 0.021 and meet Schedule 6 standards 0.066 and meet Schedule 6 standards Dieldrin 60-57-1 0.017 and meet Schedule 6 standards 0.13 and meet Schedule 6 standards E002 Wastes that are leachate toxic for Bendiocarb based on the Toxicity Characteristic Leaching Procedure. Bendiocarb 22781-23-3 NA 1.4 and meet Schedule 6 standards E003 Wastes that are leachate toxic for Benzo(a)pyrene based on the Toxicity Characteristic Leaching Procedure. Benzo(a)pyrene 50-32-8 NA 3.4 and meet Schedule 6 standards E004 Wastes that are leachate toxic for Carbaryl/Sevin/1-Naphthyl-N methyl carbamate based on the Toxicity Characteristic Leaching Procedure. Carbaryl/Sevin/1-Naphthyl-N methyl carbamate 63-25-2 NA 0.14 and meet Schedule 6 standards E005 Wastes that are leachate toxic for Carbofuran based on the Toxicity Characteristic Leaching Procedure. Carbofuran 1563-66-2 NA 0.14 and meet Schedule 6 standards E006 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for Cyanide based on the Toxicity Characteristic Leaching Procedure. Cyanides (Total)7 57-12-5 1.2 and meet Schedule 6 standards 590 and meet Schedule 6 standards Cyanides (Amenable)7 57-12-5 0.86 and meet Schedule 6 standards 30 and meet Schedule 6 standards E007 Wastes that are leachate toxic for 2,4-DCP (2,4-Dichlorophenol) based on the Toxicity Characteristic Leaching Procedure. 2,4-DCP (2,4-Dichlorophenol) 120-83-2 NA 14 and meet Schedule 6 standards E008 Wastes that are leachate toxic for DDT (total isomers) based on the Toxicity Characteristic Leaching Procedure. DDT (total isomers) NA 0.087 and meet Schedule 6 standards E009 Wastes that are leachate toxic for 1,2-Dichlorobenzene (o-Dichlorobenzene) based on the Toxicity Characteristic Leaching Procedure. 1,2-Dichlorobenzene (o-Dichlorobenzene) 95-50-1 NA 6.0 and meet Schedule 6 standards E010 Wastes that are leachate toxic for Dichloromethane (also see - methylene chloride) based on the Toxicity Characteristic Leaching Procedure. Dichloromethane (also see - methylene chloride) 75-09-02 NA 30 and meet Schedule 6 standards E011 Wastes that are leachate toxic for Methylene chloride / Dichloromethane based on the Toxicity Characteristic Leaching Procedure. Methylene chloride / Dichloromethane 75-09-02 NA 30 and meet Schedule 6 standards E012 Wastes that are leachate toxic for Dinoseb based on the Toxicity Characteristic Leaching Procedure. Dinoseb 88-85-7 NA 2.5 and meet Schedule 6 standards E013 Wastes that are leachate toxic for Dioxin & Furans based on the Toxicity Characteristic Leaching Procedure. 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin, (1,2,3,4,6,7,8-HpCDD) 35822-46-9 0.000035 and meet Schedule 6 standards 0.0025 and meet Schedule 6 standards 1,2,3,4,6,7,8-Heptachlorodibenzofuran, (1,2,3,4,6,7,8-HpCDF) 67562-39-4 0.000035 and meet Schedule 6 standards 0.0025 and meet Schedule 6 standards 1,2,3,4,7,8,9-Heptachlorodibenzofuran, (1,2,3,4,7,8,9-HpCDF) 55673-89-7 0.000035 and meet Schedule 6 standards 0.0025 and meet Schedule 6 standards HxCDDs (All Hexachlorodibenzo-p-dioxins) 34465-46-8 0.000063 and meet Schedule 6 standards 0.001 and meet Schedule 6 standards HxCDFs (All Hexachlorodibenzofurans) 55684-94-1 0.000063 and meet Schedule 6 standards 0.001 and meet Schedule 6 standards 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin, (OCDD) 3268-87-9 0.000063 and meet Schedule 6 standards 0.001 and meet Schedule 6 standards 1,2,3,4,6,7,8,9-Octachlorodibenzofuran, (OCDF) 39001-02-0 0.000063 and meet Schedule 6 standards 0.001 and meet Schedule 6 standards PeCDDs (All Pentachlorodibenzo-p-dioxins 36088-22-9 0.000063 and meet Schedule 6 standards 0.001 and meet Schedule 6 standards PeCDFs (All Pentachlorodibenzofurans) 30402-15-4 0.000035 and meet Schedule 6 standards 0.001 and meet Schedule 6 standards TCDDs (All tetachlorodibenzo-p-dioxins) 41903-57-5 0.000063 and meet Schedule 6 standards 0.001 and meet Schedule 6 standards TCDFs (All tetrachlorodibenzofurans) 55722-27-5 0.000063 and meet Schedule 6 standards 0.001 and meet Schedule 6 standards E014 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for Fluoride based on the Toxicity Characteristic Leaching Procedure. Fluoride 16984-48-8 35 and meet Schedule 6 standards NA E015 Wastes that are leachate toxic for Methyl Parathion based on the Toxicity Characteristic Leaching Procedure. Methyl Parathion 298-00-0 NA 4.6 and meet Schedule 6 standards E016 Wastes that are leachate toxic for NDMA based on the Toxicity Characteristic Leaching Procedure. NDMA 62-75-9 NA 2.3 and meet Schedule 6 standards E017 Wastes that are leachate toxic for Parathion based on the Toxicity Characteristic Leaching Procedure. Parathion 56-38-2 NA 4.6 and meet Schedule 6 standards E018 Wastes that are leachate toxic for PCBs based on the Toxicity Characteristic Leaching Procedure. Total PCBs (Sum of all PCB Isomers, or all Aroclors) 1336-36-3 0.10 and meet Schedule 6 standards 10 and meet Schedule 6 standards E019 Wastes that are leachate toxic for Phorate based on the Toxicity Characteristic Leaching Procedure. Phorate 298-02-2 NA 4.6 and meet Schedule 6 standards E020 Wastes that are leachate toxic for 2,4,5-T (2,4,5-Trichlorophenoxyacetic acid) based on the Toxicity Characteristic Leaching Procedure. 2,4,5-T (2,4,5-Trichlorophenoxyacetic acid) 93-76-5 NA 7.9 and meet Schedule 6 standards E021 Wastes that are leachate toxic for 2,3,4,6-Tetrachlorophenol /(2,3,4,6-TeCP) based on the Toxicity Characteristic Leaching Procedure. 2,3,4,6-Tetrachlorophenol /(2,3,4,6-TeCP) 58-90-2 NA 7.4 and meet Schedule 6 standards E022 Wastes that are leachate toxic for Triallate based on the Toxicity Characteristic Leaching Procedure. Triallate 2303-17-5 NA 1.4 and meet Schedule 6 standards E101 Wastes that are leachate toxic for Aldicarb based on the Toxicity Characteristic Leaching Procedure. Aldicarb 116-06-3 Meet Schedule 6 standards and best efforts to achieve 0.9 Meet Schedule 6 standards and best efforts to achieve 0.9 mg/L TCLP E102 Wastes that are leachate toxic for Atrazine + N-dealkylated metabolites (Weedex) based on the Toxicity Characteristic Leaching Procedure. Atrazine + N-dealkylated metabolites (Weedex) 1912-24-9 Meet Schedule 6 standards and best efforts to achieve 0.5 Meet Schedule 6 standards and best efforts to achieve 0.5 mg/L TCLP E103 Wastes that are leachate toxic for Azinphos-methyl based on the Toxicity Characteristic Leaching Procedure. Azinphos-methyl 86-50-0 Meet Schedule 6 standards and best efforts to achieve 2 Meet Schedule 6 standards and best efforts to achieve 2 mg/L TCLP E104 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for Boron based on the Toxicity Characteristic Leaching Procedure. Boron 7440-42-8 Meet Schedule 6 standards and best efforts to achieve 500 Meet Schedule 6 standards and best efforts to achieve 500 mg/L TCLP E105 Wastes that are leachate toxic for Bromoxynil based on the Toxicity Characteristic Leaching Procedure. Bromoxynil 1689-84-5 Meet Schedule 6 standards and best efforts to achieve 0.5 Meet Schedule 6 standards and best efforts to achieve 0.5 mg/L TCLP E106 Wastes that are leachate toxic for Chlorpyrifos based on the Toxicity Characteristic Leaching Procedure. Chlorpyrifos 2921-88-2 Meet Schedule 6 standards and best efforts to achieve 9 Meet Schedule 6 standards and best efforts to achieve 9 mg/L TCLP E107 Wastes that are leachate toxic for Cyanazine based on the Toxicity Characteristic Leaching Procedure. Cyanazine 21725-46-2 Meet Schedule 6 standards and best efforts to achieve 1 Meet Schedule 6 standards and best efforts to achieve 1 mg/L TCLP E108 Wastes that are leachate toxic for Diazinon/Phosphordithioic acid, o,o-diethyl o-(2-isopropyl 6-methyl-4-pyrimidinyl) ester based on the Toxicity Characteristic Leaching Procedure. Diazinon/Phosphordithioic acid, o,o-diethyl o-(2-isopropyl 6-methyl-4-pyrimidinyl) ester 333-41-5 Meet Schedule 6 standards and best efforts to achieve 2 Meet Schedule 6 standards and best efforts to achieve 2 mg/L TCLP E109 Wastes that are leachate toxic for Dicamba based on the Toxicity Characteristic Leaching Procedure. Dicamba 1918-00-9 Meet Schedule 6 standards and best efforts to achieve 12 Meet Schedule 6 standards and best efforts to achieve 12 mg/L TCLP E110 Wastes that are leachate toxic for Diclofop-methyl based on the Toxicity Characteristic Leaching Procedure. Diclofop-methyl 51338-27-3 Meet Schedule 6 standards and best efforts to achieve 0.9 Meet Schedule 6 standards and best efforts to achieve 0.9 mg/L TCLP E111 Wastes that are leachate toxic for Dimethoate based on the Toxicity Characteristic Leaching Procedure. Dimethoate 60-51-5 Meet Schedule 6 standards and best efforts to achieve 2 Meet Schedule 6 standards and best efforts to achieve 2 mg/L TCLP E112 Wastes that are leachate toxic for Diquat based on the Toxicity Characteristic Leaching Procedure. Diquat 231-36-7 Meet Schedule 6 standards and best efforts to achieve 7 Meet Schedule 6 standards and best efforts to achieve 7 mg/L TCLP E113 Wastes that are leachate toxic for Diuron based on the Toxicity Characteristic Leaching Procedure. Diuron 330-54-1 Meet Schedule 6 standards and best efforts to achieve 15 Meet Schedule 6 standards and best efforts to achieve 15 mg/L TCLP E114 Wastes that are leachate toxic for Glyphosate based on the Toxicity Characteristic Leaching Procedure. Glyphosate 1071-83-6 Meet Schedule 6 standards and best efforts to achieve 28 Meet Schedule 6 standards and best efforts to achieve 28 mg/L TCLP E115 Wastes that are leachate toxic for Malathion based on the Toxicity Characteristic Leaching Procedure. Malathion 121-75-5 Meet Schedule 6 standards and best efforts to achieve 19 Meet Schedule 6 standards and best efforts to achieve 19 mg/L TCLP E116 Wastes that are leachate toxic for Metolachlor based on the Toxicity Characteristic Leaching Procedure.

Metolachlor 51218-45-2 Meet Schedule 6 standards and best efforts to achieve 5 Meet Schedule 6 standards and best efforts to achieve 5 mg/L TCLP E117 Wastes that are leachate toxic for Aldicarb based on the Toxicity Characteristic Leaching Procedure. Metribuzin 21087-64-9 Meet Schedule 6 standards and best efforts to achieve 8 Meet Schedule 6 standards and best efforts to achieve 8 mg/L TCLP E118 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for Nitrate + Nitrite (as Nitrogen) based on the Toxicity Characteristic Leaching Procedure. Nitrate + Nitrite (as Nitrogen) Meet Schedule 6 standards and best efforts to achieve 1000 Meet Schedule 6 standards and best efforts to achieve 1000 mg/L TCLP E119 Wastes that are leachate toxic for Nitrilotriacetic acid (NTA) based on the Toxicity Characteristic Leaching Procedure. Nitrilotriacetic acid (NTA) 139-13-9 Meet Schedule 6 standards and best efforts to achieve 40 Meet Schedule 6 standards and best efforts to achieve 40 mg/L TCLP E120 Wastes that are leachate toxic for Paraquat based on the Toxicity Characteristic Leaching Procedure. Paraquat 4685-14-7 Meet Schedule 6 standards and best efforts to achieve 1 Meet Schedule 6 standards and best efforts to achieve 1 mg/L TCLP E121 Wastes that are leachate toxic for Picloram based on the Toxicity Characteristic Leaching Procedure. Picloram 1918-02-1 Meet Schedule 6 standards and best efforts to achieve 19 Meet Schedule 6 standards and best efforts to achieve 19 mg/L TCLP E122 Wastes that are leachate toxic for Simazine based on the Toxicity Characteristic Leaching Procedure. Simazine 122-34-9 Meet Schedule 6 standards and best efforts to achieve 1 Meet Schedule 6 standards and best efforts to achieve 1 mg/L TCLP E123 Wastes that are leachate toxic for Temephos based on the Toxicity Characteristic Leaching Procedure. Temephos 3383-96-8 Meet Schedule 6 standards and best efforts to achieve 28 Meet Schedule 6 standards and best efforts to achieve 28 mg/L TCLP E124 Wastes that are leachate toxic for Terbufos based on the Toxicity Characteristic Leaching Procedure. Terbufos 13071-79-9 Meet Schedule 6 standards and best efforts to achieve 0.1 Meet Schedule 6 standards and best efforts to achieve 0.1 mg/L TCLP E125 Wastes that are leachate toxic for Trifluralin based on the Toxicity Characteristic Leaching Procedure. Trifluralin 1582-09-8 Meet Schedule 6 standards and best efforts to achieve 4.5 Meet Schedule 6 standards and best efforts to achieve 4.5 mg/L TCLP E126 Wastes that exhibit, or are expected to exhibit, the characteristic of toxicity for uranium based on the Toxicity Characteristic Leaching Procedure. Uranium 7440-61-1 Meet Schedule 6 standards and best efforts to achieve 10 Meet Schedule 6 standards and best efforts to achieve 10 mg/L TCLP Notes to Schedule 5: 1 Treatment subcategories are shown for some wastes. In these cases, it is necessary to identify the treatment subcategory that most closely describes the particular waste for which treatment is required. The land disposal treatment requirements for that waste are those shown for that treatment subcategory. 2 Haz. Waste Number means Hazardous Waste Number. These numbers are consistent with United States Environmental Protection Agency Hazardous Waste Numbers. If there is no United States Environmental Protection Agency Hazardous Waste Number for a waste, the Hazardous Waste Number is assigned to the waste by the Ontario Ministry of the Environment. 3 CAS Number means the Chemical Abstracts Service Registry Number. When the waste or a regulated constituent is described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only. 4 See Schedule 7 for a description of the treatment methods and treatment standards associated with each treatment code. In some cases, the entries in this Schedule may set out more than one treatment code for a regulated constituent. An entry may permit a choice of treatment methods. For example, the entry “CHOXD; BIODG; or CMBST” means that the waste may be treated using any of the treatment methods that are set out for those treatment codes in Schedule 7. An entry may require treatment methods to be applied in a particular sequence. For this purpose, the abbreviation “fb” means “followed by”. For example, the entry “CHOXD fb CARBN” means that the waste must first be treated using the treatment method that is set out for CHOXD in Schedule 7 and, following that treatment, it must be treated using the treatment method that is set out for CARBN in Schedule 7. An entry may combine a choice of treatment methods and a requirement to apply treatment methods in a particular sequence (for example, “(WETOX or CHOXD) fb CARBN; or CMBST”). 5 Concentration requirements for aqueous wastes are based on analysis of composite samples. 6 Concentration requirements for non-aqueous wastes are based on analysis of grab samples. 7 Both Cyanides (Total) and Cyanides (Amenable) for non-aqueous wastes are to be analyzed using Method 9010 or 9012, found in “Test Methods for Evaluating Solid Waste, Physical/ Chemical Methods”, United States Environmental Protection Agency Publication SW–846, with a sample size of 10 grams and a distillation time of one hour and 15 minutes. O. Reg. 337/09, s. 23; O. Reg. 234/11, s. 41; O. Reg. 297/17, s. 8. Schedule 6 Universal Treatment Standards (UTS) for Characteristic Wastes A reference to this Schedule in this Regulation is a reference to the relevant Table of this Schedule, including the Notes to the Table. Table 1 Organic Constituents Column 1 Regulated Constituent: Common Name Column 2 Regulated Constituent: CAS Number Column 3 Land Disposal Treatment Requirements for Aqueous Waste: Concentration (mg/L) Column 4 Land Disposal Treatment Requirements for Non-aqueous Waste: Concentration (mg/kg, unless otherwise indicated) Acenaphthylene 208-96-8 0.059 3.4 Acenaphthene 83-32-9 0.059 3.4 Acetone 67-64-1 0.28 160 Acetonitrile 75-05-8 5.6 38 Acetophenone 96-86-2 0.010 9.7 2-Acetylaminofluorene 53-96-3 0.059 140 Acrolein 107-02-8 0.29 NA Acrylamide 79-06-1 19 23 Acrylonitrile 107-13-1 0.24 84 Aldicarb sulfone 1646-88-4 0.056 0.28 Aldrin 309-00-2 0.021 0.066 4-Aminobiphenyl 92-67-1 0.13 NA Aniline 62-53-3 0.81 14 Anthracene 120-12-7 0.059 3.4 Aramite 140-57-8 0.36 NA alpha-BHC 319-84-6 0.00014 0.066 beta-BHC 319-85-7 0.00014 0.066 delta-BHC 319-86-8 0.023 0.066 gamma-BHC 58-89-9 0.0017 0.066 Barban 101-27-9 0.056 1.4 Bendiocarb 22781-23-3 0.056 1.4 Benomyl 17804-35-2 0.056 1.4 Benzene 71-43-2 0.14 10 Benz(a)anthracene 56-55-3 0.059 3.4 Benzal chloride 98-87-3 0.055 6.0 Benzo(b)fluoranthene (difficult to distinguish from benzo(k)fluoranthene) 205-99-2 0.11 6.8 Benzo(k)fluoranthene (difficult to distinguish from benzo(b)fluoranthene) 207-08-9 0.11 6.8 Benzo(g,h,i)perylene 191-24-2 0.0055 1.8 Benzo(a)pyrene 50-32-8 0.061 3.4 Bromodichloromethane 75-27-4 0.35 15 Bromomethane/Methyl bromide 74-83-9 0.11 15 4-Bromophenyl phenyl ether 101-55-3 0.055 15 n-Butyl alcohol 71-36-3 5.6 2.6 Butylate 2008-41-5 0.042 1.4 Butyl benzyl phthalate 85-68-7 0.017 28 2-sec-Butyl-4,6-dinitrophenol (Dinoseb) 88-85-7 0.066 2.5 Carbaryl 63-25-2 0.006 0.14 Carbendazim 10605-21-7 0.056 1.4 Carbofuran 1563-66-2 0.006 0.14 Carbofuran phenol 1563-38-8 0.056 1.4 Carbon disulfide 75-15-0 3.8 4.8 mg/L TCLP Carbon tetrachloride 56-23-5 0.057 6.0 Carbosulfan 55285-14-8 0.028 1.4 Chlordane (alpha and gamma isomers) 57-74-9 0.0033 0.26 p-Chloroaniline 106-47-8 0.46 16 Chlorobenzene 108-90-7 0.057 6.0 Chlorobenzilate 510-15-6 0.10 NA 2-Chloro-1,3-butadiene 126-99-8 0.057 0.28 Chlorodibromomethane 124-48-1 0.057 15 Chloroethane 75-00-3 0.27 6.0 bis(2-Chloroethoxy)methane 111-91-1 0.036 7.2 bis(2-Chloroethyl)ether 111-44-4 0.033 6.0 Chloroform 67-66-3 0.046 6.0 bis(2-Chloroisopropyl)ether 39638-32-9 0.055 7.2 p-Chloro-m-cresol 59-50-7 0.018 14 2-Chloroethyl vinyl ether 110-75-8 0.062 NA Chloromethane/Methyl chloride 74-87-3 0.19 30 2-Chloronaphthalene 91-58-7 0.055 5.6 2-Chlorophenol 95-57-8 0.044 5.7 3-Chloropropylene 107-05-1 0.036 30 Chrysene 218-01-9 0.059 3.4 o-Cresol 95-48-7 0.11 5.6 m-Cresol (difficult to distinguish from p-cresol) 108-39-4 0.77 5.6 p-Cresol (difficult to distinguish from m-cresol) 106-44-5 0.77 5.6 m-Cumenyl methylcarbamate 64-00-6 0.056 1.4 Cyclohexanone 108-94-1 0.36 0.75 mg/L TCLP o,p'-DDD 53-19-0 0.023 0.087 p,p'-DDD 72-54-8 0.023 0.087 o,p'-DDE 3424-82-6 0.031 0.087 p,p'-DDE 72-55-9 0.031 0.087 o,p'-DDT 789-02-6 0.0039 0.087 p,p'-DDT 50-29-3 0.0039 0.087 Dibenz(a,h)anthracene 53-70-3 0.055 8.2 Dibenz(a,e)pyrene 192-65-4 0.061 NA 1,2-Dibromo-3-chloropropane 96-12-8 0.11 15 1,2-Dibromoethane/Ethylene dibromide 106-93-4 0.028 15 Dibromomethane 74-95-3 0.11 15 m-Dichlorobenzene 541-73-1 0.036 6.0 o-Dichlorobenzene 95-50-1 0.088 6.0 p-Dichlorobenzene 106-46-7 0.09 6.0 Dichlorodifluoromethane 75-71-8 0.23 7.2 1,1-Dichloroethane 75-34-3 0.059 6.0 1,2-Dichloroethane 107-06-2 0.21 6.0 1,1-Dichloroethylene 75-35-4 0.025 6.0 trans-1,2-Dichloroethylene 156-60-5 0.054 30 2,4-Dichlorophenol 120-83-2 0.044 14 2,6-Dichlorophenol 87-65-0 0.044 14 2,4-Dichlorophenoxyacetic acid/2,4-D 94-75-7 0.72 10 1,2-Dichloropropane 78-87-5 0.85 18 cis-1,3-Dichloropropylene 10061-01-5 0.036 18 trans-1,3-Dichloropropylene 10061-02-6 0.036 18 Dieldrin 60-57-1 0.017 0.13 Diethyl phthalate 84-66-2 0.20 28 p-Dimethylaminoazobenzene 60-11-7 0.13 NA 2,4-Dimethylphenol 105-67-9 0.036 14 Dimethyl phthalate 131-11-3 0.047 28 Di-n-butyl phthalate 84-74-2 0.057 28 1,4-Dinitrobenzene 100-25-4 0.32 2.3 4,6-Dinitro-o-cresol 534-52-1 0.28 160 2,4-Dinitrophenol 51-28-5 0.12 160 2,4-Dinitrotoluene 121-14-2 0.32 140 2,6-Dinitrotoluene 606-20-2 0.55 28 Di-n-octyl phthalate 117-84-0 0.017 28 Di-n-propylnitrosamine 621-64-7 0.40 14 1,4-Dioxane 123-91-1 12.0 170 Diphenylamine (difficult to distinguish from diphenylnitrosamine) 122-39-4 0.92 13 Diphenylnitrosamine (difficult to distinguish from diphenylamine) 86-30-6 0.92 13 1,2-Diphenylhydrazine 122-66-7 0.087 NA Disulfoton 298-04-4 0.017 6.2 Dithiocarbamates (total) NA 0.028 28 Endosulfan I 959-98-8 0.023 0.066 Endosulfan II 33213-65-9 0.029 0.13 Endosulfan sulfate 1031-07-8 0.029 0.13 Endrin 72-20-8 0.0028 0.13 Endrin aldehyde 7421-93-4 0.025 0.13 EPTC 759-94-4 0.042 1.4 Ethyl acetate 141-78-6 0.34 33 Ethyl benzene 100-41-4 0.057 10 Ethyl cyanide/Propanenitrile 107-12-0 0.24 360 Ethyl ether 60-29-7 0.12 160 Ethyl methacrylate 97-63-2 0.14 160 Ethylene oxide 75-21-8 0.12 NA Famphur 52-85-7 0.017 15 Fluoranthene 206-44-0 0.068 3.4 Fluorene 86-73-7 0.059 3.4 Formetanate hydrochloride 23422-53-9 0.056 1.4 Heptachlor 76-44-8 0.0012 0.066 1,2,3,4,6,7,8-Heptachlorodibenzo-p-dioxin, (1,2,3,4,6,7,8-HpCDD) 35822-46-9 0.000035 0.0025 1,2,3,4,6,7,8-Heptachlorodibenzofuran, (1,2,3,4,6,7,8-HpCDF) 67562-39-4 0.000035 0.0025 1,2,3,4,7,8,9-Heptachlorodibenzofuran, (1,2,3,4,7,8,9-HpCDF) 55673-89-7 0.000035 0.0025 Heptachlor epoxide 1024-57-3 0.016 0.066 Hexachlorobenzene 118-74-1 0.055 10 Hexachlorobutadiene 87-68-3 0.055 5.6 Hexachlorocyclopentadiene 77-47-4 0.057 2.4 HxCDDs (All Hexachlorodibenzo-p-dioxins) NA 0.000063 0.001 HxCDFs (All Hexachlorodibenzofurans) NA 0.000063 0.001 Hexachloroethane 67-72-1 0.055 30 Indeno(1,2,3-cd)pyrene 193-39-5 0.0055 3.4 Iodomethane 74-88-4 0.19 65 Isobutyl alcohol 78-83-1 5.6 170 Isodrin 465-73-6 0.021 0.066 Isosafrole 120-58-1 0.081 2.6 Kepone 143-50-0 0.0011 0.13 Methacrylonitrile 126-98-7 0.24 84 Methanol 67-56-1 5.6 0.75 mg/L TCLP Methapyrilene 91-80-5 0.081 1.5 Methiocarb 2032-65-7 0.056 1.4 Methomyl 16752-77-5 0.028 0.14 Methoxychlor 72-43-5 0.25 0.18 3-Methylcholanthrene 56-49-5 0.0055 15 4,4'-Methylene bis(2-chloroaniline) 101-14-4 0.50 30 Methylene chloride 75-09-2 0.089 30 Methyl ethyl ketone 78-93-3 0.28 36 Methyl isobutyl ketone 108-10-1 0.14 33 Methyl methacrylate 80-62-6 0.14 160 Methyl methanesulfonate 66-27-3 0.018 NA Methyl parathion 298-00-0 0.014 4.6 Metolcarb 1129-41-5 0.056 1.4 Mexacarbate 315-18-4 0.056 1.4 Molinate 2212-67-1 0.042 1.4 Naphthalene 91-20-3 0.059 5.6 2-Naphthylamine 91-59-8 0.52 NA o-Nitroaniline 88-74-4 0.27 14 p-Nitroaniline 100-01-6 0.028 28 Nitrobenzene 98-95-3 0.068 14 5-Nitro-o-toluidine 99-55-8 0.32 28 o-Nitrophenol 88-75-5 0.028 13 p-Nitrophenol 100-02-7 0.12 29 N-Nitrosodiethylamine 55-18-5 0.40 28 N-Nitrosodimethylamine 62-75-9 0.40 2.3 N-Nitroso-di-n-butylamine 924-16-3 0.40 17 N-Nitrosomethylethylamine 10595-95-6 0.40 2.3 N-Nitrosomorpholine 59-89-2 0.40 2.3 N-Nitrosopiperidine 100-75-4 0.013 35 N-Nitrosopyrrolidine 930-55-2 0.013 35 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin, (OCDD) 3268-87-9 0.000063 0.005 1,2,3,4,6,7,8,9-Octachlorodibenzofuran, (OCDF) 39001-02-0 0.000063 0.005 Oxamyl 23135-22-0 0.056 0.28 Parathion 56-38-2 0.014 4.6 Total PCBs (sum of all PCB isomers, or all Aroclors) 1336-36-3 0.10 10 Pebulate 1114-71-2 0.042 1.4 Pentachlorobenzene 608-93-5 0.055 10 PeCDDs (All Pentachlorodibenzo-p-dioxins) NA 0.000063 0.001 PeCDFs (All Pentachlorodibenzofurans) NA 0.000035 0.001 Pentachloroethane 76-01-7 0.055 6.0 Pentachloronitrobenzene 82-68-8 0.055 4.8 Pentachlorophenol 87-86-5 0.089 7.4 Phenacetin 62-44-2 0.081 16 Phenanthrene 85-01-8 0.059 5.6 Phenol 108-95-2 0.039 6.2 Phorate 298-02-2 0.021 4.6 Phthalic acid 100-21-0 0.055 28 Phthalic anhydride 85-44-9 0.055 28 Physostigmine 57-47-6 0.056 1.4 Physostigmine salicylate 57-64-7 0.056 1.4 Promecarb 2631-37-0 0.056 1.4 Pronamide 23950-58-5 0.093 1.5 Propham 122-42-9 0.056 1.4 Propoxur 114-26-1 0.056 1.4 Prosulfocarb 52888-80-9 0.042 1.4 Pyrene 129-00-0 0.067 8.2 Pyridine 110-86-1 0.014 16 Safrole 94-59-7 0.081 22 Silvex/2,4,5-TP 93-72-1 0.72 7.9 1,2,4,5-Tetrachlorobenzene 95-94-3 0.055 14 TCDDs (All Tetrachlorodibenzo-p-dioxins) NA 0.000063 0.001 TCDFs (All Tetrachlorodibenzofurans) NA 0.000063 0.001 1,1,1,2-Tetrachloroethane 630-20-6 0.057 6.0 1,1,2,2-Tetrachloroethane 79-34-5 0.057 6.0 Tetrachloroethylene 127-18-4 0.056 6.0 2,3,4,6-Tetrachlorophenol 58-90-2 0.030 7.4 Thiodicarb 59669-26-0 0.019 1.4 Thiophanate-methyl 23564-05-8 0.056 1.4 Toluene 108-88-3 0.080 10 Toxaphene 8001-35-2 0.0095 2.6 Triallate 2303-17-5 0.042 1.4 Tribromomethane/Bromoform 75-25-2 0.63 15 1,2,4-Trichlorobenzene 120-82-1 0.055 19 1,1,1-Trichloroethane 71-55-6 0.054 6.0 1,1,2-Trichloroethane 79-00-5 0.054 6.0 Trichloroethylene 79-01-6 0.054 6.0 Trichlorofluoromethane 75-69-4 0.020 30 2,4,5-Trichlorophenol 95-95-4 0.18 7.4 2,4,6-Trichlorophenol 88-06-2 0.035 7.4 2,4,5-Trichlorophenoxyacetic acid/ 2,4,5-T 93-76-5 0.72 7.9 1,2,3-Trichloropropane 96-18-4 0.85 30 1,1,2-Trichloro-1,2,2-trifluoroethane 76-13-1 0.057 30 Triethylamine 121-44-8 0.081 1.5 Tris(2,3-Dibromopropyl) phosphate 126-72-7 0.11 0.1 Vernolate 1929-77-7 0.042 1.4 Vinyl chloride 75-01-4 0.27 6.0 Xylenes-mixed isomers (sum of o-, m-, and p-xylene concentrations) 1330-20-7 0.32 30 Notes to Table 1: 1. CAS Number means the Chemical Abstracts Service Registry Number. When the waste or a regulated constituent is described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only. 2. Concentration requirements for aqueous wastes are expressed in mg/L and are based on analysis of composite samples. 3. Concentration requirements for non-aqueous wastes are based on analysis of grab samples. Table 2 Inorganic Constituents Column 1 Regulated Constituent: Common Name Column 2 Regulated Constituent: CAS Number Column 3 Land Disposal Treatment Requirements for Aqueous Waste: Concentration (mg/L) Column 4 Land Disposal Treatment Requirements for Non-aqueous Waste: Concentration (mg/kg, unless otherwise indicated) Antimony 7440-36-0 1.9 1.15 mg/L TCLP Arsenic 7440-38-2 1.4 5.0 mg/L TCLP Barium 7440-39-3 1.2 21 mg/L TCLP Beryllium 7440-41-7 0.82 1.22 mg/L TCLP Cadmium 7440-43-9 0.69 0.11 mg/L TCLP Chromium (Total) 7440-47-3 2.77 0.60 mg/L TCLP Cyanides (Total) 57-12-5 1.2 590 Cyanides (Amenable) 57-12-5 0.86 30 Lead 7439-92-1 0.69 0.75 mg/L TCLP Mercury-Non-aqueous waste from Retort 7439-97-6 NA 0.20 mg/L TCLP Mercury-All Others 7439-97-6 0.15 0.025 mg/L TCLP Nickel 7440-02-0 3.98 11 mg/L TCLP Silver 7440-22-4 0.43 0.14 mg/L TCLP Thallium 7440-28-0 1.4 0.20 mg/L TCLP Notes to Table 2: 1. CAS Number means the Chemical Abstracts Service Registry Number. When the waste or a regulated constituent is described as a combination of a chemical with its salts or esters, the CAS number is given for the parent compound only. 2. Concentration requirements for aqueous wastes are expressed in mg/L and are based on analysis of composite samples. 3. Concentration requirements for non-aqueous wastes are based on analysis of grab samples. 4. Both Cyanides (Total) and Cyanides (Amenable) for non-aqueous wastes are to be analyzed using Method 9010 or 9012, found in “Test Methods for Evaluating Solid Waste, Physical/ Chemical Methods”, United States Environmental Protection Agency Publication SW–846, with a sample size of 10 grams and a distillation time of one hour and 15 minutes. O. Reg. 297/17, s. 9. Schedule 7 TREATMENT METHODS AND Standards Treatment Code Treatment Method and Treatment Standard ADGAS Venting of compressed gases into an absorbing or reacting medium (i.e., solid or liquid) — venting can be accomplished through physical release utilizing valves/piping; physical penetration of the container; or penetration through detonation. AMLGM Amalgamation of liquid, elemental mercury contaminated with radioactive materials utilizing inorganic reagents such as copper, zinc, nickel, gold, and sulphur that result in a nonliquid, semi-solid amalgam and thereby reducing potential emissions of elemental mercury vapours to the air. BIODG Biodegradation of organics or non-metallic inorganics (i.e., degradable inorganics that contain the elements of phosphorus, nitrogen, and sulphur) in units operated under either aerobic or anaerobic conditions such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., Total Organic Carbon can often be used as an indicator parameter for the biodegradation of many organic constituents that cannot be directly analyzed in aqueous waste residues). CARBN Carbon adsorption (granulated or powdered) of non-metallic inorganics, organo-metallics, or organic constituents, operated such that a surrogate compound or indicator parameter has not undergone breakthrough (e.g., Total Organic Carbon can often be used as an indicator parameter for the adsorption of many organic constituents that cannot be directly analyzed in aqueous waste residues). Breakthrough occurs when the carbon has become saturated with the constituent (or indicator parameter) and substantial change in adsorption rate associated with that constituent occurs. CHOXD Chemical or electrolytic oxidation utilizing the following oxidation reagents (or waste reagents) or combinations of reagents: (1) Hypochlorite (e.g., bleach); (2) chlorine; (3) chlorine dioxide; (4) ozone or UV (ultraviolet light) assisted ozone; (5) peroxides; (6) persulphates; (7) perchlorates; (8) permangantes; or (9) other oxidizing reagents of equivalent efficiency, performed in units operated such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., Total Organic Carbon can often be used as an indicator parameter for the oxidation of many organic constituents that cannot be directly analyzed in aqueous waste residues). Chemical oxidation specifically includes what is commonly referred to as alkaline chlorination. CHRED Chemical reduction utilizing the following reducing reagents (or waste reagents) or combinations of reagents: (1) Sulphur dioxide; (2) sodium, potassium, or alkali salts or sulphites, bisulphites, metabisulphites, and polyethylene glycols (e.g., NaPEG and KPEG); (3) sodium hydrosulphide; (4) ferrous salts; or (5) other reducing reagents of equivalent efficiency, performed in units operated such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., Total Organic Halogens can often be used as an indicator parameter for the reduction of many halogenated organic constituents that cannot be directly analyzed in aqueous waste residues). Chemical reduction is commonly used for the reduction of hexavalent chromium to the trivalent state. CMBST High temperature organic destruction technologies, such as combustion in incinerators, boilers, industrial furnaces; and certain non-combustive technologies, such as the Catalytic Extraction Process. DEACT Deactivation to remove the hazardous characteristics of a waste due to its ignitability, corrosivity, or reactivity. FSUBS Fuel substitution in units operated in accordance with applicable technical operating requirements. HLVIT Vitrification of high level mixed radioactive wastes in units in compliance with all applicable radioactive protection requirements under control of the Canadian Nuclear Safety Commission. IMERC Incineration of wastes containing organics and mercury. All aqueous waste and non-aqueous waste residues derived from this process must then comply with the corresponding treatment standards per waste code with consideration of any applicable subcategories (e.g., High or Low Mercury Subcategories). INCIN Incineration. LLEXT Liquid-liquid extraction (often referred to as solvent extraction) of organics from liquid wastes into an immiscible solvent for which the regulated constituents have a greater solvent affinity, resulting in an extract high in organics that must undergo either incineration, reuse as a fuel, or other recovery/reuse and a raffinate (extracted liquid waste) proportionately low in organics that must undergo further treatment as specified in the standard. MACRO Macroencapsulation with surface coating materials such as polymeric organics (e.g., resins and plastics) or with a jacket of inert inorganic materials to substantially reduce surface exposure to potential leaching media. Macroencapsulation specifically does not include any material that would be classified as a tank or container. NEUTR Neutralization with the following reagents (or waste reagents) or combinations of reagents: (1) Acids; (2) bases; or (3) water (including aqueous wastes) resulting in a pH greater than 2 but less than 12.5 as measured in the aqueous residuals. NLDBR No land disposal based on recycling. POLYM Formation of complex high-molecular weight solids through polymerization of monomers in high-TOC D001 non-aqueous wastes which are chemical components in the manufacture of plastics. PRECP Chemical precipitation of metals and other inorganics as insoluble precipitates of oxides, hydroxides, carbonates, sulphides, sulphates, chlorides, fluorides, or phosphates. The following reagents (or waste reagents) are typically used alone or in combination: (1) Lime (i.e., containing oxides or hydroxides of calcium or magnesium; (2) caustic (i.e., sodium or potassium hydroxides; (3) soda ash (i.e., sodium carbonate); (4) sodium sulphide; (5) ferric sulphate or ferric chloride; (6) alum; or (7) sodium sulphate. Additional flocculating, coagulation or similar reagents/ processes that enhance sludge dewatering characteristics are not precluded from use. RBERY Thermal recovery of Beryllium. RCGAS Recovery/reuse of compressed gases including techniques such as reprocessing of the gases for reuse/resale; filtering/adsorption of impurities; remixing for direct reuse or resale; and use of the gas as a fuel source. RCORR Recovery of acids or bases utilizing one or more of the following recovery technologies: (1) Distillation (i.e., thermal concentration); (2) ion exchange; (3) resin or solid adsorption; (4) reverse osmosis; or (5) incineration for the recovery of acid — Note: this does not preclude the use of other physical phase separation or concentration techniques such as decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies. RLEAD Thermal recovery of lead in secondary lead smelters. RMERC Retorting or roasting in a thermal processing unit capable of volatilizing mercury and subsequently condensing the volatilized mercury for recovery. All aqueous waste and non-aqueous waste residues derived from this process must then comply with the corresponding treatment standards per waste code with consideration of any applicable subcategories (e.g., High or Low Mercury Subcategories). RMETL Recovery of metals or inorganics utilizing one or more of the following technologies: (1) Ion exchange; (2) resin or solid (i.e., zeolites) adsorption; (3) reverse osmosis; (4) chelation/solvent extraction; (5) freeze crystalization; (6) ultrafiltration or (7) simple precipitation (i.e., crystalization) — Note: This does not preclude the use of other physical phase separation or concentration techniques such as decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies. RORGS Recovery of organics utilizing one or more of the following technologies: (1) Distillation; (2) thin film evaporation; (3) steam stripping; (4) carbon adsorption; (5) critical fluid extraction; (6) liquid-liquid extraction; (7) precipitation/crystalization (including freeze crystallization); or (8) chemical phase separation techniques (i.e., addition of acids, bases, demulsifiers, or similar chemicals); — Note: this does not preclude the use of other physical phase separation techniques such as decantation, filtration (including ultrafiltration), and centrifugation, when used in conjunction with the above listed recovery technologies. RTHRM Thermal recovery of metals or inorganics from non-aqueous wastes in units identified as industrial furnaces. RZINC Resmelting in high temperature metal recovery units for the purpose of recovery of zinc. STABL Stabilization with the following reagents (or waste reagents) or combinations of reagents: (1) Portland cement; or (2) lime/pozzolans (e.g., fly ash and cement kiln dust) — this does not preclude the addition of reagents (e.g., iron salts, silicates, and clays) designed to enhance the set/cure time or compressive strength, or to overall reduce the leachability of the metal or inorganic. SSTRP Steam stripping of organics from liquid wastes utilizing direct application of steam to the wastes operated such that liquid and vapour flow rates, as well as temperature and pressure ranges have been optimized, monitored, and maintained. These operating parameters are dependent upon the design parameters of the unit such as the number of separation stages and the internal column design. This results in a condensed extract high in organics that must undergo either incineration, reuse as a fuel, or other recovery/reuse and an extracted aqueous waste that must undergo further treatment as specified in the standard. WETOX Wet air oxidation performed in units operated such that a surrogate compound or indicator parameter has been substantially reduced in concentration in the residuals (e.g., Total Organic Carbon can often be used as an indicator parameter for the oxidation of many organic constituents that cannot be directly analyzed in aqueous waste residues). WTRRX Controlled reaction with water for highly reactive inorganic or organic chemicals with precautionary controls for protection of workers from potential violent reactions as well as precautionary controls for potential emissions of toxic/ignitable levels of gases released during the reaction. O. Reg. 461/05, s. 27. Schedule 8 Alternative Treatment for Hazardous Debris A reference to this Schedule in this Regulation is a reference to the relevant Table of this Schedule, including the Notes to the Table. Table 1 Extraction Technologies Treatment Method Standard Debris and Contaminant Restrictions Physical Extraction - Abrasive Blasting: Removal of contaminated debris surface layers using water or air pressure to propel a solid abrasive (e.g., steel shot, aluminum oxide grit, plastic beads). For Glass, Metal, Plastic, Rubber: Treatment to a clean debris surface. For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Removal of at least 0.6 cm of the surface layer; treatment to a clean debris surface. No Restrictions Physical Extraction - Scarification, Grinding, and Planing: Process utilizing striking piston heads, saws, or rotating grinding wheels such that contaminated debris surface layers are removed. For Glass, Metal, Plastic, Rubber: Treatment to a clean debris surface. For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Removal of at least 0.6 cm of the surface layer; treatment to a clean debris surface. No Restrictions Physical Extraction - Spalling: Drilling or chipping holes at appropriate locations and depth in the contaminated debris surface and applying a tool which exerts a force on the sides of those holes such that the surface layer is removed. The surface layer removed remains subject to the debris treatment standards. For Glass, Metal, Plastic, Rubber: Treatment to a clean debris surface. For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Removal of at least 0.6 cm of the surface layer; treatment to a clean debris surface. No Restrictions Physical Extraction - Vibratory Finishing: Process utilizing scrubbing media, flushing fluid, and oscillating energy such that hazardous contaminants or contaminated debris surface layers are removed. For Glass, Metal, Plastic, Rubber: Treatment to a clean debris surface. For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Removal of at least 0.6 cm of the surface layer; treatment to a clean debris surface. No Restrictions Physical Extraction - High Pressure Steam and Water Sprays: Application of water or steam sprays of sufficient temperature, pressure, residence time, agitation, surfactants, and detergents to remove hazardous contaminants from debris surfaces or to remove contaminated debris surface layers. For Glass, Metal, Plastic, Rubber: Treatment to a clean debris surface. For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Removal of at least 0.6 cm of the surface layer; treatment to a clean debris surface. No Restrictions Chemical Extraction - Water Washing and Spraying: Application of water sprays or water baths of sufficient temperature, pressure, residence time, agitation, surfactants, acids, bases, and detergents to remove hazardous contaminants from debris surfaces and surface pores or to remove contaminated debris surface layers. For all Debris: Treatment to a clean debris surface; For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (½ inch) in one dimension (i.e., thickness limit); debris surfaces must be in contact with water solution for at least 15 minutes; For debris contaminated with a dioxin-characteristic waste, treatment must be carried out in accordance with an environmental compliance approval, despite any exemptions that might otherwise apply. For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Restricted unless the contaminant is soluble to at least 5% by weight in water solution or 5% by weight in emulsion. Chemical Extraction - Liquid Phase Solvent Extraction: Removal of hazardous contaminants from debris surfaces and surface pores by applying a non-aqueous liquid or liquid solution which causes the hazardous contaminants to enter the liquid phase and be flushed away from the debris along with the liquid or liquid solution while using appropriate agitation, temperature, and residence time. For all Debris: Treatment to a clean debris surface; For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (½ inch) in one dimension (i.e., thickness limit) ; debris surfaces must be in contact with water solution for at least 15 minutes; For debris contaminated with a dioxin-characteristic waste, treatment must be carried out in accordance with an environmental compliance approval, despite any exemptions that might otherwise apply. For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Restricted unless the contaminant is soluble to at least 5% by weight in the solvent. Chemical Extraction - Vapour Phase Solvent Extraction: Application of an organic vapour using sufficient agitation, residence time, and temperature to cause hazardous contaminants on contaminated debris surfaces and surface pores to enter the vapour phase and be flushed away with the organic vapour. For all Debris: Treatment to a clean debris surface; For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (½ inch) in one dimension (i.e., thickness limit) ; debris surfaces must be in contact with the organic vapour for at least 60 minutes; For debris contaminated with a dioxin-characteristic waste, treatment must be carried out in accordance with an environmental compliance approval, despite any exemptions that might otherwise apply. For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Restricted unless the contaminant is soluble to at least 5% by weight in the solvent. Thermal Extraction - High Temperature Metals Recovery: Application of sufficient heat, residence time, mixing, fluxing agents, or carbon in a smelting, melting, or refining furnace to separate metals from debris. Separate metal from treated debris; For debris contaminated with a dioxin-characteristic waste, treatment must be carried out in accordance with an environmental compliance approval, despite any exemptions that might otherwise apply. No Restrictions Thermal Extraction - Thermal Desorption: Heating in an enclosed chamber under either oxidizing or nonoxidizing atmospheres at sufficient temperature and residence time to vaporize hazardous contaminants from contaminated surfaces and surface pores and to remove the contaminants from the heating chamber in a gaseous exhaust gas. For all Debris: Vaporize hazardous contaminants from contaminated surfaces and surface pores and remove the contaminants from the heating chamber in a gaseous exhaust gas. This must be done in accordance with an environmental compliance approval, despite any exemptions that might otherwise apply. For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 10 cm (4 inches) in one dimension (i.e., thickness limit). For all Debris: Restricted for metal contaminants other than mercury. Notes to Table 1: 1. Where a contaminant restriction is set out for a treatment method and type of debris, the use of that treatment method is not sufficient if that type of debris contains the restricted contaminant. If the restricted treatment is used, the debris must also be treated by another treatment method that is described in the Schedule and for which no restriction is set out for that type of debris and contaminant. 2. “Clean debris surface” means that the surface, when viewed without magnification, must be free of all visible contaminated soil and hazardous waste, except that residual staining from soil and waste that consists of light shadows, slight streaks or minor discolorations may be present, and soil and waste in cracks, crevices or pits may be present, if the residual staining or the waste and soil in cracks, crevices or pits is limited to not more than 5% of each square inch of surface area. 3. Thickness Limit for Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: If reducing the particle size of debris to meet the treatment standards results in material that no longer meets the 60 mm minimum particle size limit for debris, the material is subject to the waste-specific treatment standards for the waste contaminating the material, unless the debris has been cleaned and separated from contaminated soil and waste prior to size reduction. Alternative thickness limits may be used by obtaining an environmental compliance approval. Table 2 Destruction Technologies Treatment Method Standard Restrictions Biological Destruction (Biodegradation): Removal of hazardous contaminants from debris surfaces and surface pores in an aqueous solution and biodegradation of organic or nonmetallic inorganic compounds (i.e., inorganics that contain phosphorus, nitrogen, or sulphur) in units operated under either aerobic or anaerobic conditions. For all Debris: Removal of hazardous contaminants and biodegradation of organic or nonmetallic inorganic compounds. This must be done in accordance with an environmental compliance approval, despite any exemptions that might otherwise apply. For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (1\2 inch) in one dimension (i.e., thickness limit). For all Debris: Restricted for metal contaminants. Chemical Destruction: Chemical Oxidation: Chemical or electrolytic oxidation utilizing the following oxidation reagents (or waste reagents) or combination of reagents: - hypochlorite (e.g., bleach); - chlorine; - chlorine dioxide; - ozone or UV (ultraviolet light) assisted ozone; - peroxides; - persulphates; - perchlorates; - permanganates; - other oxidizing reagents of equivalent destruction efficiency. Chemical oxidation specifically includes what is referred to as alkaline chlorination. For all Debris: Chemical or electrolytic oxidation. This must be done in accordance with an environmental compliance approval, despite any exemptions that might otherwise apply. For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (1\2 inch) in one dimension (i.e., thickness limit). For all Debris: Restricted for metal contaminants. Chemical Destruction: Chemical Reduction: Chemical reaction utilizing the following reducing reagents (or waste reagents) or combination of reagents: - sulphur dioxide; - sodium, potassium, or alkali salts of sulphites, bisulphites, and metabisulphites, and polyethylene glycols (e.g., NaPEG and KPEG); - sodium hydrosulphide; - ferrous salts; - other reducing reagents of equivalent efficiency. For all Debris: Chemical Reduction. This must be done in accordance with an environmental compliance approval, despite any exemptions that might otherwise apply. For Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: Debris must be no more than 1.2 cm (1\2 inch) in one dimension (i.e., thickness limit). For all Debris: Restricted for metal contaminants. Thermal Destruction: Thermal treatment, excluding Thermal Desorption units. For all Debris: Thermal destruction or vitrification. This must be done in accordance with an environmental compliance approval, despite any exemptions that might otherwise apply. For Brick, Concrete, Glass, Metal, Pavement, Rock: Restricted for metal contaminants other than mercury, except that there are no metal restrictions for vitrification. Notes to Table 2: 1. Where a contaminant restriction is set out for a treatment method and type of debris, the use of that treatment method is not sufficient if that type of debris contains the restricted contaminant. If the restricted treatment is used, the debris must also be treated by another treatment method that is described in the Schedule and for which no restriction is set out for that type of debris and contaminant. 2. Thickness Limit for Brick, Cloth, Concrete, Paper, Pavement, Rock, Wood: If reducing the particle size of debris to meet the treatment standards results in material that no longer meets the 60 mm minimum particle size limit for debris, the material is subject to the waste-specific treatment standards for the waste contaminating the material, unless the debris has been cleaned and separated from contaminated soil and waste prior to size reduction. Alternative thickness limits may be used by obtaining an environmental compliance approval. Table 3 Immobilization Technologies Treatment Method Standard Restriction Macroencapsulation: Application of surface coating materials such as polymeric organics (e.g., resins and plastics) or use of a jacket of inert inorganic materials to substantially reduce surface exposure to potential leaching media. Encapsulating material must completely encapsulate debris and be resistant to degradation by the debris and its contaminants and materials into which it may come into contact after placement (leachate, other waste, microbes), and substantially reduce surface exposure to potential leaching media. No Restrictions Microencapsulation: Stabilization of the debris with the following reagents (or waste reagents) such that the leachability of the contaminants is reduced: - Portland cement; - lime/pozzolans (e.g., fly ash and cement kiln dust). Reagents (e.g., iron salts, silicates, and clays) may be added to enhance the set/cure time or compressive strength, or to reduce the leachability of the contaminants. Leachability of the contaminants must be reduced. No Restrictions Sealing: Application of an appropriate material which adheres tightly to the debris surface to avoid exposure of the surface to potential leaching media. When necessary to effectively seal the surface, sealing entails pretreatment of the debris surface to remove foreign matter and to clean and roughen the surface. Sealing materials include epoxy, silicone, and urethane compounds, but paint may not be used as a sealant. Sealing must avoid exposure of the debris surface to potential leaching media and sealant must be resistent to degradation by the debris and its contaminants and materials into which it may come into contact after placement (leachate, other waste, microbes). No Restrictions Note to Table 3: 1. Note re: microencapsulation: If reducing the particle size of debris to meet the treatment standards results in material that no longer meets the 60 mm minimum particle size limit for debris, the material is subject to the waste-specific treatment standards for the waste contaminating the material, unless the debris has been cleaned and separated from contaminated soil and waste prior to size reduction. Alternative thickness limits may be used by obtaining an environmental compliance approval. O. Reg. 297/17, s. 10. Schedule 9 TEST METHOD FOR THE DETERMINATION OF “LIQUID WASTE” (SLUMP TEST)* (1) Sampling Obtain a representative sample of the waste to be tested. (2) Equipment 2.1 Mould — the representative waste sample shall be formed in a mould, in the form of the frustum of a cone with the base 200 mm in diameter, the top 100 mm in diameter, and the height 300 mm. The base and the top shall be open and parallel to each other and at right angles to the axis of the cone. The mould shall be made of a metal that is chemically resistant to the wastes to be tested and that has a thickness that is at least 1.5 mm. It shall be provided with foot pieces and handles as shown in Figure 1. 2.2 Tamping Rod — the rod shall be round, straight and steel with a diameter of 16 mm and a length of 600 mm. One end shall be rounded to a hemispherical tip with a diameter of 16 mm. (3) Procedure 3.1 Dampen the mould and place it on a flat, moist, non-absorbent (rigid) surface. Hold the mould firmly in place during filling by standing on the two foot pieces. From the sample of the material obtained, immediately fill the mould in three layers, each approximately one-third the volume of the mould. Notes: 1) The test must be carried out at a temperature of not less than 10°C. 2) One-third of the volume of the slump mould fills it to a depth of 70 mm. Two-thirds of the volume fills it to a depth of 160 mm. 3.2 Rod each layer with 25 strokes of the tamping rod. Uniformly distribute the strokes over the cross-section of each layer. For the bottom layer this will necessitate inclining the rod slightly and making approximately half of the strokes near the perimeter, and then progressing with vertical strokes spirally toward the center. Rod layers throughout their depth. For the second layer and the top layer, the strokes must just penetrate into the underlying layers. 3.3 When filling and rodding the top layer, heap the material above the mould before rodding is started. If the rodding operation results in subsidence of the material below the top edge of the mould, add additional material to maintain an excess of material above the top of the mould. After the top layer has been rodded, the excess material shall be screeded off to the level of the top of the mould. Remove the spilled material from the base of the mould. 3.4 Withdraw the mould immediately from the material by raising it carefully in a vertical direction. The operation of raising the mould shall be performed in approximately 5 seconds by a steady upward lift with no lateral or torsional motion. The entire operation from the start of the filling through removal of the mould shall be carried out without interruption and shall be completed within 2 minutes. 3.5 Determine the slump immediately after by measuring the difference between the height of the mould and the average height of the top surface of the material after subsidence. Notes: 1) Waste samples that break or slump laterally give incorrect results. When this condition occurs, the test shall be repeated with a new sample. 2) If two consecutive tests on a sample of material show a falling away or shearing off of a portion of the material from the mass of the specimen, the material probably lacks necessary plasticity and cohesiveness for the slump test to be applicable. 3) Duplicate tests on two different portions of the sample should not vary more than 10 mm. (4) Report 4.1 Record the slump in millimeters to the nearest 10 mm of subsidence of the sample during the test. * The method is based on the Canadian Standards Association test method for determining the slump of concrete (A23.2-5C) O. Reg. 558/00, s. 5; O. Reg. 461/05, s. 26. Schedules 10-13 Revoked: O. Reg. 297/17, s. 11.