Provided by CCOHS/produit par le CCHST

General -- Waste Management

R.R.O. 1990, Reg. 347

As amended by: O. Reg. 183/92; 240/92; 501/92; 555/92; 457/93; 507/93; 105/94; 190/94; 298/94; 299/94; 512/95; 128/98; 157/98; 191/98; 460/99; 558/00

Section 1 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 having a generic name listed 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 a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of approval does not have characteristics similar to the characteristics of the acute hazardous waste chemical from which it was derived;

"agricultural waste" means waste, other than sewage, resulting from farm operations, including animal husbandry and where a farm operation is carried on in respect of food packing, food preserving, animal slaughtering or meat packing, includes the waste from such operations;

"asbestos waste" means solid or liquid waste that results from the removal of asbestos-containing construction or insulation materials or the manufacture of asbestos-containing products and contains asbestos in more than a trivial amount or proportion;

"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;

"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 subparagraph i, ii or iii, does not include a waste stream or waste material contaminated with material of the specified generic name;

"composting" means the treatment of waste by aerobic decomposition of organic matter by bacterial action for the production of stabilized humus;

"corrosive waste" means a waste that,

(a) 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, or

(b) 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;

"cover material" means soil or other material approved for use in sealing cells in landfilling;

"dead animal" means an animal that dies naturally or from disease or by reason of accident and includes parts thereof;

"derelict motor vehicle" means a motor vehicle that,

(a) is inoperable, and

(b) has no market value as a means of transportation, or, has a market value as a means of transportation that is less than the cost of repairs required to put it into operable condition;

"Director" means the Director of the Waste Management Policy Branch of the Ministry and includes an alternate named by him or her;

"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 a certificate of approval or provisional certificate of approval for 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;

"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;

"fly-ash" means particulate matter removed from combustion flue gases;

"generator" means the operator of a waste generation facility;

"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 the 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 from a sewage works approved under section 53 of the Ontario Water Resources Act that is conveyed away from the site where it is produced by a sewer approved under that section, or

(ii) waste in a vehicle sewage holding tank;

"hazardous industrial waste" means,

(a) a generic or specific waste listed 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 a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of 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 or the Atomic Energy Control Board,

(i) pathological waste,

(j) leachate toxic waste, or

(k) PCB waste as defined in Regulation 362 of the Revised Regulations of Ontario, 1990,

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 subject to an agreement with a municipality under theOntario 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 having a generic name listed 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 a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of approval does not have characteristics similar to the characteristics of the hazardous waste chemical from which it was derived;

"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 an ignitable compressed gas (Class 2, Division D as defined in the regulations under the Transportation of Dangerous Goods Act (Canada), or

(d) is an oxidizing substance (Class 5, Divisions 1 and 2) as defined in the regulations under the Transportation of Dangerous Goods Act (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 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, or

(e) schools, laboratories or hospitals;

"inert fill" means earth or rock fill or waste of a similar nature that contains no putrescible materials or soluble or decomposable chemical substances;

"intact manifest" means a manifest as provided by the Ministry, with all six parts intact;

"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;

"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, Method 1311 that appears in the 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 an equivalent test method approved by the Director;

"liquid industrial waste" means waste that is both liquid waste and industrial waste but does not include,

(a) hauled sewage,

(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,

(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 a sewage works subject to the Ontario Water Resources Act or established before the 3rd day of April, 1957 or into a sewage system, as defined in Part VIII of the Act,

(f) waste that results directly from food processing and preparation operations, including food packing, food preserving, wine making, cheese making and restaurants,

(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;

"manifest" means a numbered document in Form 1 that was obtained from the Ministry;

"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;

"metal finishing" Repealed. [O. Reg. 558/00, s. 1]

"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);

"municipal waste incinerator site" Repealed. [O. Reg. 512/95, s. 1]

"non-hazardous solid industrial waste" means industrial waste that is not liquid industrial waste and is not hazardous waste and includes asbestos waste;

"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;

"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 a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of approval does not have characteristics similar to the characteristics of pathological waste referred to in clause (a), (b) or (c);

"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 a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of 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,

(h) is an explosive (Class 1) as defined in the regulations under the Transportation of Dangerous Goods Act (Canada);

"receiver" means the operator of any facility to which waste is transferred by a carrier;

"Regional Director" means a Director appointed under section 5 of the Act and responsible for a region established by the Ministry for administrative purposes, but does not mean the Director of the Waste Management Branch of the Ministry or an alternate named by him or her;

"scavenging" means the uncontrolled removal of reusable material from waste at a waste disposal site;

"Section 39 Director" means a Director appointed under section 5 of the Act for purposes of section 39 of the Act;

"severely toxic waste" means,

(a) a waste that contains a contaminant listed 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 a certificate of approval that states that, in the opinion of the Section 39 Director, the waste that is produced in accordance with the certificate of 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;

"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, and

(b) hazardous waste,

but does not include waste from the servicing of motor vehicles at a retail motor vehicle service station or service facility that has a written agreement for the collection and management of such waste with a waste management system approved under Part V of the Act for the purposes and does not include waste from,

(c) a nursing home under the Nursing Homes Act,

(d) a home under the Homes for the Aged and Rest Homes Act,

(e) a home for special care under the Homes for Special Care Act,

(f) the professional office of a member of the Royal College of Dental Surgeons of Ontario, or

(g) the professional office of a member of the College of Physicians and Surgeons of Ontario;

"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;

"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 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 or waste described in clause (p), (q), (r), (s), (t) or (u) of the definition of "hazardous waste" in section 1 or in clause (d) of the definition of "liquid industrial waste" in section 1,

(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 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 incinerated or wholly utilized as a fuel or fuel supplement in a combustion unit.

(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. 240/92, s. 1; 501/92, s. 1; 555/92, s. 1; 105/94, s. 1; 190/94, s. 1; 512/95, s. 1; 157/98, s. 1; 460/99, s. 1; 558/00, s. 1]

DESIGNATION AND EXEMPTION OF WASTES

Section 2

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.

(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.

(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. 555/92, s. 2; 105/94, s. 2; 128/98, s. 1; 157/98, s. 2]

Section 3

3. (1) The following wastes are exempted from Part V of the Act and this Regulation:

1. Agricultural wastes.

2. Condemned animals or parts thereof at a plant licensed under the Meat Inspection Act (Ontario) or an establishment operating under the Meat Inspection Act (Canada).

3. Dead animals to which the Dead Animal Disposal Act applies.

4. Repealed. [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).

(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, transferred by a generator for direct transportation to a site,

i. to be wholly used 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,

ii. to be promptly packaged for retail sale to meet a realistic market demand, or

iii. 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, 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.

(3) Despite subsection (1), material referred to in subparagraph i of paragraph 1 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 agreeing to accept the material, specifying what use will be made of it and stipulating that the process or operation described in that subparagraph is ongoing at the time the material is being transported.

(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. 105/94, s. 3; 128/98, s. 2; 157/98, s. 3]

CLASSIFICATION AND EXEMPTION OF WASTE DISPOSAL SITES

4. Revoked. [O. Reg. 105/94, s. 4]

Section 5

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. Derelict motor vehicle sites.

4. Incinerators at the site of a crematorium within the meaning of the Cemeteries Act.

(2) Dust suppression sites designated in a certificate of approval or provisional certificate of approval for a dust suppression waste management system and established and operated in accordance therewith are exempt from the requirement to have a waste disposal site certificate of approval or provisional certificate of approval.

(3) Revoked. [O. Reg. 555/92, s. 4]

(4) No person shall use waste oil as a dust suppressant.

[O. Reg. 555/92, s. 4]

Section 5.1

5.1 (1) A waste disposal site that is the subject of an application for a certificate of approval referred to in subsection 30(1) of the Act is exempt from the requirements of subsection 30(1) of the Act, but only in relation to the application, and only if the application is not for an approval for,

(a) the deposit of waste at a dump;

(b) the landfilling of waste; or

(c) the incineration of waste.

(2) For the purposes of clause (1)(a), the deposit of waste at a dump does not include the handling, storing, transferring, treating or processing of waste at a dump.

[O. Reg. 457/93, s. 1]

Section 5.2

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 a certificate of approval or a provisional certificate of approval, to receive municipal waste.

(2) A municipality that owns or operates a landfilling site is exempt from sections 27, 30 and 32 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.

(3) A municipality that owns or operates a landfilling site is exempt from sections 30 and 32 of the Act with respect to an increase in the rate at which municipal waste may be received at the site from areas within its service area.

(4) If a municipality owns or operates a landfilling site that has been filled in accordance with an exemption under this section, the municipality is exempt from sections 27, 30 and 32 with respect to increasing the service area of another landfilling site that it owns and operates if the additional area from which the other site will receive municipal waste is part or all of the area from which the filled site received municipal waste.

(5) A person, other than a municipality, who owns or operates a landfilling site is exempt from sections 27, 30 and 32 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 a certificate of approval or a provisional certificate of approval, the terms or conditions of which establish a periodic quantity limit for deliveries of waste to the landfilling site.

(6) A person, other than a municipality, who owns or operates a landfilling site is exempt from sections 30 and 32 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;

(c) the site has a certificate of approval or a provisional certificate of 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. 299/94, s. 1]

Section 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.

(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).

(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 incinerated or buried at the site.

(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.

(5) Revoked. [O. Reg. 183/92, s. 1]

[O. Reg. 183/92, s. 1; 555/92, s. 5]

CLASSIFICATION AND EXEMPTION OF WASTE MANAGEMENT SYSTEMS

Section 7

7. Section 27 of the Act does not apply to vehicle sewage holding tanks.

[O. Reg. 157/98, s. 4]

Section 8

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.

(2) Waste generation facilities are exempt from the requirement to have a waste management system certificate of approval in respect of the production, collection, handling and temporary storage of waste.

(3) Section 27 of the Act does not apply in respect of trucks for hauling used tires.

[O. Reg. 105/94, s. 6]

Section 9

9. The standards, procedures and requirements set out in this Regulation do not apply to the extent that terms and conditions set out in a certificate of approval or a provisional certificate of approval issued under section 39 of the Act impose different standards, procedures or requirements.

Section 10

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.

STANDARDS FOR WASTE DISPOSAL SITES

Section 11

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.

Section 12

12. The following are prescribed as standards for the location, maintenance and operation of an incineration site:

1. The location of the incineration 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. the TRICIL Limited landfilling site located on Lot 9, Concession 10, Township of Moore, County of Lambton, or

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. a certificate of approval or provisional certificate of approval issued after the 1st day of January, 1990, or

B. an amendment to a certificate of approval or provisional certificate of approval made after the 1st day of January, 1990.

4. The incinerator 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 incinerator are available, including facilities for the disposal of residue and of quenching and scrubbing water.

5. The design and capacity of the incinerator shall be in accordance with accepted engineering practices and 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 an incinerator.

7. The incineration 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 incineration 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.

12.1 Repealed. [O. Reg. 512/95, s. 2]

Section 13

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.

Section 14

14. (1) Subject to subsection (2), no dump shall be established or operated in a city, borough, town, separated town, township, village or police village in any county, regional municipality or the County of Haliburton.

(2) A dump may be established in the following parts of Ontario:

1. The townships of Albemarle, Eastnor, Lindsay and St. Edmunds, in the County of Bruce.

2. The townships of Barrie, Bedford, Clarendon and Miller, Howe Island, Kennebec, Olden and Palmerston and North and South Canonto, in the County of Frontenac.

3. The townships of Bangor, Wicklow and McClure, Carlow, Dungannon, Elzevir and Grimsthorpe, Herschel, Limerick, Madoc, Marmora and Lake, Mayo, Monteagle, Tudor and Cashel, and Wollaston, in the County of Hastings.

4. The townships of Dalhousie and North Sherbrooke, Darling, Lavant, North Burgess, and South Sherbrooke, in the County of Lanark.

5. The townships of Asphodel, Belmont and Methuen, Chandos, Ennismore, Galway and Cavendish, and Harvey, in the County of Peterborough.

6. The townships of Bagot and Blithfield, Brougham, Brudenell and Lyndoch, Griffith and Matawatchan, Head, Clara, and Maria, North Algona, Radcliffe, Raglan, Sebastopol, and South Algona, in the County of Renfrew.

7. The townships of Carden, Dalton, and Laxton, Digby and Longford, in the County of Victoria.

8. The Improvement District of Bicroft, the townships of Anson, Hindon and Minden, Cardiff, Dysart, Bruton, Clyde, Dudley, Eyre, Guilford, Harburn, Harcourt and Havelock, Glamorgan, Lutterworth, Monmouth, Sherborne, McClintock and Livingstone, and Snowdon and Stanhope, in the County of Haliburton.

(3) No dump shall be established or operated in the following parts of the territorial districts of Ontario:

1. The City of Sault Ste. Marie, the towns of Blind River, Bruce Mines, Thessalon and Elliot Lake, and the villages of Hilton Beach and Iron Bridge, in the Territorial District of Algoma.

2. The City of Timmins, the towns of Cochrane, Hearst, Iroquois Falls, Kapuskasing and Smooth Rock Falls, and the townships of Glackmeyer, Tisdale and Whitney, in the Territorial District of Cochrane.

3. The towns of Dryden, Keewatin, Kenora, and Sioux Lookout, and the townships of Jaffray and Melick, in the Territorial District of Kenora.

4. The towns of Gore Bay and Little Current, in the Territorial District of Manitoulin.

5. That part of the District Municipality of Muskoka that, on the 31st day of December, 1970, was the towns of Bala, Bracebridge, Gravenhurst and Huntsville, and the villages of Port Carling, Port Sydney and Windermere.

6. The City of North Bay, the towns of Cache Bay, Mattawa and Sturgeon Falls, and the townships of Bonfield, East Ferris, Field and Springer, in the Territorial District of Nipissing.

7. The towns of Kearney, Parry Sound, Powassan and Trout Creek, the villages of Burk's Falls, Magnetawan, Rosseau, South River and Sundridge, and the townships of Foley, McDougall, North Himsworth, and South Himsworth, in the Territorial District of Parry Sound.

8. The towns of Fort Frances and Rainy River, and the Township of Atikokan, in the Territorial District of Rainy River.

9. That part of The Regional Municipality of Sudbury and the Territorial District of Sudbury that, on the 31st day of December, 1972, was the City of Sudbury, the towns of Capreol, Coniston, Copper Cliff, Espanola, Levack, Lively, Massey and Webbwood, and the townships of Balfour, Falconbridge, and Neelon and Garson, in the Territorial District of Sudbury.

10. The City of Thunder Bay, the Town of Geraldton and the townships of Beardmore, Manitowadge, Neebing, Nipigon, Oliver, Paipoonge, Schreibel, Shuniah, and Terrace Bay, and the improvement districts of Nakina and Red Rock, in the Territorial District of Thunder Bay.

11. The towns of Charlton, Cobalt, Englehart, Haileybury, Kirkland Lake, Latchford, and New Liskeard, the Village of Thornloe, and the townships of Armstrong, Bucke, Larder Lake and McGarry, in the Territorial District of Timiskaming.

Section 14.1

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 a certificate of approval for the site, obtain written authorization from the owner for the proposed use of the site.

[O. Reg. 157/98, s. 5]

Section 15

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.

STANDARDS FOR WASTE MANAGEMENT SYSTEMS

Section 16

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.

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 certificate of approval or provisional certificate of 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 certificate of approval or provisional certificate of 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 (Canada).

9. The driver of a waste transportation vehicle used for the transportation of 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 certificate of approval or provisional certificate of approval that authorizes the transportation.

11. Where a waste transportation vehicle is used for transporting municipal waste, a copy of the certificate of approval or provisional certificate of 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 a certificate of approval, provisional certificate of approval or order.

(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 that is exempt from the requirement of having a certificate of approval or provisional certificate of approval.

(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.

(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.

(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. 105/94, s. 7; 157/98, s. 6]

Section 16.1

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

Section 17

17. 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 operating under a certificate of approval or provisional certificate of 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 operating under a certificate of approval or provisional certificate of 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.

GENERATOR REGISTRATION

Section 18

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 an initial Generator Registration Report in Form 2 to the Director in respect of the waste generation facility and each subject waste the generator produces, collects, handles or stores or is likely to produce, collect, handle or store.

(2) Every report referred to in subsection (1) or (4) shall comply with the Manual and shall contain such data, analysis and information as will enable the Director to satisfy himself or herself as to the quality and nature of the waste.

(3) Upon receipt of an initial Generator Registration Report, the Director shall issue to the generator a generator registration document with a generator registration number and the applicable waste numbers accepted by the Director.

(4) Where there is a change from the information submitted in the initial Generator Registration Report or any previous supplementary Generator Registration Reports in respect of name, address, or telephone number, addition of subject wastes or significant change in the description or physical or chemical characteristics of the subject wastes, the generator who submitted the applicable report shall send a supplementary Generator Registration Report to the Director within fifteen days after the change.

(5) No generator shall transfer a particular subject waste to a waste transportation system until the generator has obtained a generator registration document with a waste number for that waste.

(6) If a change that is required to be reported by subsection (4) involves the variation of a subject waste or the production, collection, handling or storage of a new subject waste, the generator shall not transfer the subject waste to a waste transportation system until the reissue of the generator registration document specifically addressing the change has been obtained.

(7) Every generator shall use the generator registration number and applicable waste numbers set out in the Manual in all transfers of subject waste under this Regulation.

(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.

(9) A record referred to in subsection (8) may be disposed of after two years.

(10) When any subject waste is retained at a waste generation facility for a period longer than three months, the generator, unless there is a waste disposal site certificate of approval or provisional certificate of approval in respect of the facility, shall submit a report to the Regional Director of the Ministry within five business days after the three month period which report shall comply with the Manual and shall include the name and waste number of the waste, the quantity involved, the manner in which it is stored, the reasons for the retention and the anticipated time and manner of disposal of the waste.

(11) Every generator who transfers subject waste to a waste transportation system shall orally report to the Director any transferred subject waste that the generator is not able, within four weeks, to confirm was delivered to the intended receiving facility or to another receiving facility approved to accept the waste.

(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 Regional Director of the Ministry or an alternate named by him or her may assign a generator registration number or accept a waste number identified by the generator.

(13) Where a generator registration number is assigned under subsection (12), subsection (5) does not apply and subsections (1) and (2) shall be complied with within ninety days.

(14) Where a waste number is accepted under subsection (12), subsections (5) and (6) do not apply.

(15) For purposes of this section,

"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 5.

[O. Reg. 105/94, s. 8; 460/99, s. 2; 558/00, s. 2]

MANIFESTS -- GENERATOR REQUIREMENTS

Section 19

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 operating under a certificate of approval or provisional certificate of approval 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 subject to the Ontario Water Resources Act or established before the 3rd day of August, 1957 or to a sewage system as defined in Part VIII of the Environmental Protection Act.

(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 (Canada).

[O. Reg. 460/99, s. 3]

MANIFESTS -- CARRIER REQUIREMENTS

Section 20

20. Every carrier shall report to the Director the number of every intact manifest supplied to the carrier that is lost, spoiled or used other than in accordance with this Regulation.

Section 21

21. (1) No carrier shall have possession of subject waste unless the carrier has, accompanying the waste, a manifest in respect of the waste, completed by the generator in accordance with the Manual and this Regulation, except during a transfer while the manifest is being completed by a generator or receiver.

(2) For purposes of subsection (1), a manifest is not completed by a generator in accordance with this Regulation if it contains an obvious error.

[O. Reg. 460/99, s. 4]

Section 22

22. (1) No carrier shall permit subject waste to pass from the carrier's control except in accordance with this Regulation.

(2) A carrier, with the specific approval of a Regional Director of the Ministry or an alternate named by him or her, may transfer subject waste in Ontario to another vehicle in the same waste transportation system or to a waste transportation system operating under a certificate of approval or provisional certificate of approval or to a receiving facility to alleviate a dangerous situation.

(3) Where a truckload or less of subject waste has been transferred by a generator to a waste transportation system, the carrier shall promptly 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.

MANIFESTS -- TRANSPORT WITHIN ONTARIO

Section 23

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.

(2) Where subject waste is transferred to a waste transportation system by a generator,

(a) for each truckload or part thereof transferred, the carrier shall complete section B (Carrier) of an intact manifest and give the manifest, at the time of the transfer, to the generator; and

(b) for each truckload or part thereof transferred, the generator shall obtain from the carrier the intact manifest, with section B completed, and shall,

(i) at the time of the transfer, complete section A (Generator), in accordance with the Manual,

(ii) remove Copy 1 (White) and return it to the Director within three working days after the transfer,

(iii) remove Copy 2 (Green) and retain it for a period of two years, and

(iv) return the remaining four copies of the manifest to the carrier at the time of the transfer.

(3) A carrier may transfer subject waste,

(a) with the specific approval of a Regional Director of the Ministry or an alternate named by him or her, to another vehicle of the same waste transportation system, to a waste transportation system operating under a certificate of approval or provisional certificate of approval or to a specified receiving facility as mentioned in clause (b), (c) or (d) to alleviate a dangerous situation;

(b) to a waste disposal site operating under a certificate of approval or provisional certificate of approval authorizing acceptance of the waste;

(c) with the consent of the owner of the sewage works, to a sewage works for which an approval under the Ontario Water Resources Act has been issued and that is not in contravention of the approval; or

(d) to a waste-derived fuel site having a combustion unit operating under a certificate of approval issued under section 9 of the Act authorizing acceptance and combustion of the waste.

(4) Every carrier transferring waste under subsection (3) shall, at the time of the transfer, give the receiver the remaining four parts of the applicable manifest completed for that load of waste.

(5) Where a transfer of subject waste takes place under subsection (3), the receiver shall obtain from the carrier the remaining four parts of the manifest completed for that load and shall,

(a) at the time of the transfer, complete section C (Receiver) of the remaining four parts of the manifest;

(b) remove Copy 3 (Yellow) of the manifest and return it to the Director within three working days after the transfer;

(c) remove Copy 4 (Pink) of the manifest and return it to the carrier at the time of the transfer;

(d) retain Copy 5 (Blue) of the manifest for two years; and

(e) remove Copy 6 (Brown) of the manifest and return it to the generator shown on the manifest within three working days after the transfer.

(6) Every carrier transferring waste under subsection (3) shall, prior to leaving the site of the transfer, obtain from the receiver of the waste Copy 4 (Pink) of the manifest referred to under clause (5)(c) and shall retain it for a period of two years.

(7) Every carrier who is the operator of a waste transportation system for which a certificate of approval or provisional certificate of approval as a dust suppression waste management system is issued may deposit for the purpose of dust suppression, in accordance with the approval, dust suppressant at a dust suppression site designated in the approval and, where that is done, shall,

(a) at the time of completion of the deposit, complete section C (Receiver) of the remaining four parts of the applicable manifest received under subclause (2)(b)(iv);

(b) remove Copy 3 (Yellow) of the manifest and return it to the Director within three working days after the deposit;

(c) retain Copy 4 (Pink) of the manifest for two years; and

(d) remove Copy 6 (Brown) of the manifest and return it to the generator shown on the manifest within three working days after the deposit.

[O. Reg. 460/99, s. 5; 558/00, s. 3]

MANIFESTS -- TRANSPORT OUT OF ONTARIO

Section 24

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.

(2) Where subject waste is transferred for transport to a receiving facility in a Canadian jurisdiction, a manifest issued under the Transportation of Dangerous Goods Act (Canada) or an equivalent manifest issued by a Canadian jurisdiction may be used for purposes of compliance with this Regulation.

(3) Where subject waste is transferred for transport to a receiving facility in a Canadian jurisdiction and the laws of that jurisdiction require submission to authorities in that jurisdiction of the equivalent of Copy 1 or 3 of a manifest, submission to the Director of a photocopy of the copy submitted or of a copy retained may be substituted for the requirement to submit Copy 1 or 3 of a manifest.

(4) Where subject waste is transferred to a waste transportation system by a generator,

(a) for each truckload or portion thereof transferred, the carrier shall complete section B (Carrier) of an intact manifest and give the manifest, at the time of the transfer, to the generator; and

(b) for each truckload or portion thereof transferred, the generator shall obtain from the carrier the intact manifest, with section B completed, and shall,

(i) at the time of the transfer, complete section A (Generator) in accordance with the Manual,

(ii) remove Copy 1 (White) and return it to the Director within three working days after the transfer,

(iii) remove Copy 2 (Green) and retain it for two years, and

(iv) return the remaining four copies of the manifest to the carrier at the time of the transfer.

(5) 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 complete section C (Receiver) of the applicable manifest completed for that load of waste.

(6) Every carrier transferring subject waste to a receiving facility outside Ontario shall, at the time of the transfer, give the receiver the remaining four parts of the applicable manifest for completion of section C (Receiver).

(7) Every carrier who transfers waste under subsection (6) shall,

(a) return Copy 3 (Yellow) of the manifest to the Director within three working days after the transfer;

(b) retain Copy 4 (Pink) of the manifest for two years; and

(c) remove Copy 6 (Brown) of the manifest and return it to the generator indicated on the manifest within three working days after the transfer.

(8) Every manifest referred to in subsection (7) shall have section C (Receiver) completed by the receiver.

[O. Reg. 460/99, s. 6]

MANIFESTS -- TRANSPORT INTO ONTARIO

Section 25

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.

(2) Where subject waste is transferred in Canada for transport to a receiving facility in Ontario, a manifest under the Transportation of Dangerous Goods Act (Canada) or any equivalent manifest issued by a Canadian jurisdiction may be used for purposes of compliance with this Regulation.

(3) No carrier shall bring subject waste into Ontario for purposes of transport to a receiving facility in Ontario unless,

(a) the waste was accepted from a generator who has a generator registration document specifying a generator registration number and the applicable waste numbers under section 18 unless section 18 does not apply to that generator;

(b) for each truckload or portion thereof to be transferred, the carrier completed section B (Carrier) of an intact manifest and gave it, at the time of the transfer, to the generator for completion of section A (Generator) and return to the carrier; and

(c) the applicable manifest with section B (carrier) completed by the carrier and section A (Generator) completed by the generator accompanies the waste.

(4) Every carrier who brings subject waste into Ontario for transfer to a receiving facility in Ontario shall forward to the Director, within three working days after the out of province transfer, Copy 1 (White) of the applicable manifest showing the generator registration number and the applicable waste number.

(5) A carrier may transfer subject waste,

(a) to a waste disposal site operating under a certificate of approval or provisional certificate of approval authorizing acceptance of the waste;

(b) with the consent of the owner of the sewage works, to a sewage works for which an approval under the Ontario Water Resources Act has been issued, and that is not in contravention of the approval; or

(c) to a waste-derived fuel site having a combustion unit operating under a certificate of approval issued under section 9 of the Act authorizing acceptance and combustion of the waste.

(6) Every carrier transferring waste under subsection (5) shall, at the time of the transfer, give the receiver the remaining four parts of the applicable manifest completed in respect of the waste.

(7) Where a transfer of subject waste takes place under subsection (5), the receiver shall obtain from the carrier the remaining four parts of the manifest completed in respect of that load of waste and shall,

(a) at the time of the transfer, complete section C (Receiver) of the remaining four parts of the manifest;

(b) remove Copy 3 (Yellow) of the manifest and return it to the Director within three working days after the transfer;

(c) remove Copy 4 (Pink) of the manifest and return it to the carrier at the time of the transfer;

(d) retain Copy 5 (Blue) of the manifest for two years; and

(e) remove Copy 6 (Brown) of the manifest and return it to the generator shown on the manifest within three working days after the transfer.

(8) Every carrier who has transferred waste under subsection (5) shall, prior to leaving the site of the transfer, obtain from the receiver Copy 4 (Pink) of the applicable manifest and shall retain it for two years.

(9) Every carrier who is the operator of a waste transportation system for which a certificate of approval or provisional certificate of approval as a dust suppression waste management system is issued may deposit for the purpose of dust suppression, in accordance with the approval, dust suppressant at a dust suppression site designated in the approval and, where that is done, shall,

(a) at the time of completion of the deposit, complete section C (Receiver) of the remaining four parts of the manifest accompanying the waste;

(b) remove Copy 3 (Yellow) of the manifest and return it to the Director within three working days after the deposit;

(c) retain Copy 4 (Pink) of the manifest for two years; and

(d) remove Copy 6 (Brown) of the manifest and return it to the generator shown on the manifest within three working days after the deposit.

MANIFESTS -- TRANSPORT THROUGH ONTARIO

Section 26

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 completed in accordance with the requirements of the jurisdiction issuing the manifest.

(2) Where this section applies, a manifest issued under the Transportation of Dangerous Goods Act (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.

REFUSALS

Section 27

27. (1) A receiver who refuses to accept a transfer of subject waste shall prepare a refusal report indicating the manifest number, the generator registration number, the carrier number and the reason for refusal and return it to the Director within three working days after the refusal.

(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.

(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 section A (Generator) of the applicable manifest and the carrier shall, at the time of the transfer, give the generator four parts of the applicable manifest completed by the generator in accordance with this Regulation.

(4) Every generator shall accept a transfer of unadulterated subject waste in the circumstances described in subsection (3).

(5) Where a transfer of subject waste occurs under subsection (3), the generator shall obtain from the carrier the remaining four parts of the applicable manifest completed by the generator in accordance with this Regulation and shall,

(a) at the time of the transfer, complete section C (Receiver) of the remaining four parts of the manifest;

(b) return Copy 3 (Yellow) to the Director within three working days after the transfer;

(c) return Copy 4 (Pink) to the carrier at the time of the transfer; and

(d) retain Copy 6 (Brown) for two years.

(6) Every carrier who has transferred waste under subsection (3) shall, prior to leaving the site of the transfer, obtain from the receiver Copy 4 (Pink) of the applicable manifest and shall retain it for two years.

(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.

ON-SITE INCINERATORS

Section 28

28. (1) On-site incinerators are exempt from the operation of section 27 of the Act on condition that no hazardous waste or liquid industrial waste is incinerated therein.

(2) On-site incinerators are exempt from the requirement of being the subject-matter of a hearing under subsection 30(1) of the Act.

(3) This section does not apply to woodwaste combustor sites or waste-derived fuel sites.

[O. Reg. 555/92, s. 7]

WOODWASTE COMBUSTOR SITES

Section 28.1

28.1 (1) A woodwaste combustor site for residential heating is exempt from section 27 of the Act if not more than fifty cubic metres of woodwaste is stored at the woodwaste combustor site at any time.

(2) A woodwaste combustor site is exempt from section 27 of the Act

(a) not more than 500 cubic metres of woodwaste is stored at the woodwaste combustor site at any time;

(b) not more than 100 tonnes of woodwaste is combusted at the woodwaste combustor site on any day; and

(c) none of the woodwaste stored at the woodwaste combustor site is stored there for more than six months.

(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.

(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.

(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]

Section 28.2

28.2 (1) A woodwaste combustor site is exempt from the requirement of being the subject-matter of a hearing under subsection 30(1) of the Act if not more than 100 tonnes of woodwaste is combusted at the woodwaste combustor site on any day.

(2) A woodwaste combustor site is exempt from the requirement of being the subject-matter of a hearing under subsection 30(1) of the Act if the heat from the combustion is recovered and utilized.

[O. Reg. 555/92, s. 8; 191/98, s. 1]

WASTE-DERIVED FUEL SITES

Section 28.3

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.

(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.

(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.

(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]

Section 28.4

28.4 A waste-derived fuel site is exempt from the requirement of being the subject-matter of a hearing under subsection 30(1) of the Act if not more than ten tonnes of waste-derived fuel is utilized at the site on any day.

[O. Reg. 555/92, s. 8]

Section 28.5

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.

(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]

EXISTING HOSPITAL INCINERATORS

Section 29

29. (1) Existing hospital incinerators are exempt from the operation of section 27 of the Act in respect of their establishment, use and operation.

(2) The exemption granted in subsection (1) in respect of any incinerator within the class is conditional on a submission being made, in respect of the incinerator, to the Director, before the end of March in each year, of a report on the preceding year ending with the 31 st day of December setting out a summary of the source, nature and quantity of waste incinerated therein and a professional assessment of the extent of compliance with Regulation 346 of Revised Regulations of Ontario, 1990 in the operation of the incinerator.

STATIONARY REFRIGERANT WASTE

Section 30

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 with a certificate of approval or provisional certificate of approval to handle stationary refrigerant waste.

(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 with a certificate of approval or provisional certificate of approval to handle stationary refrigerant waste.

(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.

[O. Reg. 190/94, s. 2]

Section 31

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.

(2) A wholesale dealer in refrigerants shall keep a written record each time that it receives or transports stationary refrigerant waste.

(3) A stationary refrigerant waste recycler shall keep a written record each time that it receives or recycles stationary refrigerant waste.

(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.

(5) A record made under this section may be disposed of after two years.

(6) Revoked. [O. Reg. 190/94, s. 3]

[O. Reg. 190/94, s. 3]

Section 32

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.

(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.

Section 33

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 a certificate of approval or provisional certificate of approval under Part V of the Act.

Section 34

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 with a certificate of approval or provisional certificate of approval to handle stationary refrigerant waste; or

(b) the waste generation facility is operated by a wholesale dealer in refrigerants.

Section 35

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 27.

MOBILE REFRIGERANT WASTE

Section 36

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.

(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.

Section 37

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 with a certificate of approval or provisional certificate of approval to handle mobile refrigerant waste.

(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.

[O. Reg. 190/94, s. 4]

Section 38

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.

(2) A mobile refrigerant waste recycler shall keep a written record each time that it receives or recycles mobile refrigerant waste.

(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.

(4) A record made under this section may be disposed of after two years.

(5) Revoked. [O. Reg. 190/94, s. 5]

[O. Reg. 190/94, s. 5]

Section 39

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.

(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.

Section 40

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 a certificate of approval or provisional certificate of approval under Part V of the Act.

Section 41

41. Section 18 does not apply in respect of subject waste that is mobile refrigerant waste.

Section 42

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 34.

SELECTED WASTE DEPOTS

Section 43

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]

Section 44

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:

Table

COLUMN A COLUMN B
1. anti-freeze 1. waste anti-freeze
2. lubricant 2. waste lubricant
3. oil filters 3. waste oil filters

(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]

Section 45

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 or 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.

(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]

Section 46

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).

(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).

(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]

Section 47

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 as defined in subsection 1.2.1 of Regulation 454 of the Revised Regulations of Ontario, 1990 and to the Regional Director responsible for the region in which the depot is located.

(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.

(3) Each operator and owner of a selected waste depot shall notify the Chief Fire Official and the Regional 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]

Section 48

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]

Section 49

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

Section 50

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]

Section 51

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.

(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]

Section 52

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.

(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]

Section 53

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]

Section 54

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.

(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]

Section 55

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.

(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]

Section 56

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.

(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).

(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.

(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]

Section 57

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.

(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]

Section 58

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.

(2) An agreement under subsection (1) shall be between an operator or owner of the depot and a party to whom a certificate of approval or provisional certificate of approval has been issued under Part V of the Act authorizing the party 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 party under the agreement.

(3) An agreement under subsection (1) shall state the following:

1. The name and address of an owner or operator of the depot.

2. The name and address of the party responsible for removing waste, the type of selected waste to be removed by the party and the number of the certificate of approval or provisional certificate of approval that authorizes the party to transport the type of waste.

3. The name, address and telephone number of an individual able to answer questions about the implementation of the agreement on behalf of the party responsible for removing the waste.

4. The approximate time intervals at which the party responsible for removing the waste will remove the waste.

5. The expiry date of the agreement.

(4) Each operator and owner of a selected waste depot shall ensure that selected waste is removed from the depot only by a party to an agreement under subsection (1) to whom a certificate of approval or provisional certificate of approval has been issued authorizing the removal of the waste.

(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. 298/94, s. 1]

Section 59

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.

(2) Each operator and owner of a selected waste depot shall ensure that written notice is given to the Chief Fire Official as defined in subsection 1.2.1 of Regulation 454 of the Revised Regulations of Ontario, 1990 and to the Regional 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.

(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.

(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.

(5) Each operator and owner of a selected waste depot shall ensure that the Chief Fire Official and the Regional 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]

Section 60

60. In the event of conflict between sections 44 to 59 and the provisions of Regulation 532 of the Revised Regulations of Ontario, 1990 or Regulation 454 of the Revised Regulations of Ontario, 1990, the provisions of Regulation 532 and Regulation 454 prevail.

[O. Reg. 298/94, s. 1]

PESTICIDE CONTAINER DEPOTS

Section 61

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]

Section 62

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.

(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]

Section 63

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).

(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]

Section 64

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 Regional Director responsible for the region in which the pesticide container depot is located.

(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.

(3) Each operator and owner of a pesticide container depot shall notify in writing the Regional Director responsible for the region in which the pesticide container 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]

Section 65

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]

Section 66

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]

Section 67

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]

Section 68

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.

(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]

Section 69

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]

Section 70

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]

Section 71

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]

Section 72

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.

(2) An agreement under subsection (1) shall be between an operator or owner of the depot and a party to whom a certificate of approval or provisional certificate of approval has been issued under Part V of the Act authorizing the party to transport the empty pesticide containers to be removed from the depot.

(3) The agreement 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 party responsible for removing the empty pesticide containers and the number of the certificate of approval or provisional certificate of approval that authorizes the party to transport them.

3. The name, address and telephone number of an individual able to answer questions about the implementation of the agreement on behalf of the party responsible for removing the empty pesticide containers.

4. The approximate time intervals at which the party responsible for removing the waste will remove the waste.

5. The expiry date of the agreement.

(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 party to an agreement under subsection (1) to whom a certificate of approval or provisional certificate of approval has been issued authorizing the removal of the waste.

(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. 298/94, s. 1]

Section 73

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.

(2) Each operator and owner of a pesticide container depot shall ensure that written notice is given to the Regional 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 empty pesticide containers.

(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.

(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.

(5) Each operator and owner of a pesticide container depot shall ensure that the Regional Director responsible for the region in which the depot is located is given timely written notice of the address referred to in subsection (4).

[O. Reg. 298/94, s. 1]

Form 1

Form 2

Form 2 (continued)

Schedule 1 HAZARDOUS INDUSTRIAL WASTES

Hazardous Industrial Waste from Non-Specific Sources

USEPA Hazardous Waste No. Industry and No. Waste
F001 NA9301 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.
F002 NA9302 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.
F003 NA9303 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.
F004 NA9304 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.
F005 NA9305 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.
F006 NA9306 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.
F007 NA9308 Spent cyanide plating bath solutions from electroplating operations
F008 NA9309 Plating bath residues from the bottom of plating baths from electroplating operations where cyanides are used in the process.
F009 NA9310 Spent stripping and cleaning bath solutions from electroplating operations where cyanides are used in the process.
F010 NA9311 Quenching bath residues from oil baths from metal heat treating operations where cyanides are used in the process.
F011 NA9312 Spent cyanide solutions from salt bath pot cleaning from metal heat treating operations.
F012 NA9313 Quenching waste water treatment sludges from metal heat treating operations where cyanides are used in the process.
F019 NA9307 Wastewater treatment sludges from the chemical conversion coating of aluminum except from zirconium phosphating in aluminum can washing when such phosphating is an exclusive conversion coating process.
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.).
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.
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.
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.).
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 Schedules 2A or 2B.).
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.
F026 Wastes (except wastewater and spent carbon rom 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.
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.).
F028 Residues resulting from the incineration or thermal treatment of soil contaminated with EPA Hazardous Waste Nos. F020, F021, F022, F023, F026 and F027.
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. 261.35 1 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.
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.
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.
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) 1 (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) 1 , if those residuals are to be disposed of.
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) 1 (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.
F039 Leachate (liquids that have percolated through land disposed wastes) resulting from the disposal of more than one restricted waste classified as hazardous under subpart D of this part. (Leachate resulting from the disposal of one or more of the following EPA Hazardous Wastes and no other Hazardous Wastes retains its EPA Hazardous Waste Number(s): F020, F021, F022, F026, F027, and/or F028.).

Hazardous Industrial Waste from Specific Sources

USEPA Hazardous Waste No. Industry and No. Waste
Wood preservation:
K001 NA9316 Bottom sediment sludge from the treatment of wastewaters from wood preserving processes that use creosote and/or pentachlorophenol.
Inorganic pigments:
K002 NA9317 Wastewater treatment sludge from the production of chrome yellow and orange pigments.
K003 NA9318 Wastewater treatment sludge from the production of molybdate orange pigments.
K004 NA9319 Wastewater treatment sludge from the production of zinc yellow pigments.
K005 NA9320 Wastewater treatment sludge from the production of chrome green pigments.
K006 NA9321 Wastewater treatment sludge from the production of chrome oxide green pigments (anhydrous and hydrated).
K007 NA9322 Wastewater treatment sludge from the production of iron blue pigments.
K008 NA9323 Oven residue from the production of chrome oxide green pigments.
Organic chemicals:
K009 NA9324 Distillation bottoms from the production of acetaldehyde from ethylene.
K010 NA9325 Distillation side cuts from the production of acetaldehyde from ethylene.
K011 NA9326 Bottom stream from the wastewater stripper in the production of acrylonitrile.
K013 NA9327 Bottom stream from the acetonitrile column in the production of acrylonitrile.
K014 NA9328 Bottoms from the acetonitrile purification column in the production of acrylonitrile.
K015 NA9329 Still bottoms from the distillation of benzyl chloride.
K016 NA9330 Heavy ends or distillation residues from the production of carbon tetrachloride.
K017 NA9331 Heavy ends (still bottoms) from the purification column in the production of epichlorohydrin.
K018 NA9332 Heavy ends from the fractionation column in ethyl chloride production.
K019 NA9333 Heavy ends from the distillation of ethylene dichloride in ethylene dichloride production.
K020 NA9334 Heavy ends from the distillation of vinyl chloride in vinyl chloride monomer production.
K021 NA9335 Aqueous spent antimony catalyst waste from fluoromethanes production.
K022 NA9336 Distillation bottom tars from the production of phenol/acetone from cumene.
K023 NA9337 Distillation light ends from the production of phthalic anhydride from naphthalene.
K024 NA9338 Distillation bottoms from the production of phthalic anhydride from naphthalene.
K025 NA9341 Distillation bottoms from the production of nitrobenzene by the nitration of benzene.
K026 NA9342 Stripping still tails from the production of methyl ethyl pyridines.
K027 NA9343 Centrifuge and distillation residues from toluene diisocyanate production.
K028 NA9344 Spent catalyst from the hydrochlorinator reactor in the productions of 1,1,1trichloroethane.
K029 NA9345 Waste from the product stream stripper in the production of 1,1,1trichloroethane.
K030 NA9348 Column bottoms or heavy ends from the combined production of trichloroethylene and perchloroethylene.
K083 NA9349 Distillation bottoms from aniline production.
K085 NA9352 Distillation or fractionation column bottoms from the production of chlorobenzenes.
K093 NA9339 Distillation light ends from the production of phthalic anhydride from orthoxylene.
K094 NA9340 Distillation bottoms from the production of phthalic anhydride from orthoxylene.
K095 NA9346 Distillation bottoms from the production of 1,1,1trichloroethane.
K096 NA9347 Heavy ends from the heavy ends column from the production of 1,1,1trichloroethane.
K103 NA9350 Process residues from aniline extraction from the production of aniline.
K104 NA9351 Combined wastewater streams generated from nitrobenzene/aniline production.
K105 NA9353 Separated aqueous stream from the reactor product washing step in the production of chlorobenzenes.
K107 Column bottoms from product separation from the production of 1,1-dimethyl-hydra-zine (UDMH) from carboxylic acid hydrazines.
K108 Condensed column overheads from product separation and condensed reactor vent gases from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
K109 Spent filter cartridges from product purification from the production of 1, 1- dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
K110 Condensed column overheads from intermediate separation from the production of 1,1-dimethylhydrazine (UDMH) from carboxylic acid hydrazides.
K111 Product washwaters from the production of dinitrotoluene via nitration of toluene.
K112 Reaction by-product water from the drying column in the production of toluenediamine via hydrogenation of dinitrotoluene.
K113 Condensed liquid light ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.
K114 Vicinals from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.
K115 Heavy ends from the purification of toluenediamine in the production of toluenediamine via hydrogenation of dinitrotoluene.
K116 Organic condensate from the solvent recovery column in the production of toluene diisocyanate via phosgenation of toluenediamine.
K117 Wastewater from the reactor vent gas scrubber in the production of ethylene dibromide via bromination of ethene.
K118 Spent adsorbent solids from purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.
K136 Still bottoms from the purification of ethylene dibromide in the production of ethylene dibromide via bromination of ethene.
K140 Floor sweepings, off-specification product and spent filter media from the production of 2,4,6-tribromophenol.
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.)
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.
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.
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.).
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.)
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.).
K159 Organics from the treatment of thiocarbamate wastes.
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.)

Hazardous Industrial Waste from Specific Sources...cont'd

USEPA Hazardous Waste No. Industry and No. Waste
Inorganic chemicals:
K071 NA9390 Brine purification muds from the mercury cell process in chlorine production, where separately prepurified brine is not used.
K073 NA9391 Chlorinated hydrocarbon waste from the purification step of the diaphragm cell process using graphite anodes in chlorine production.
K106 NA9392 Wastewater treatment sludge from the mercury cell process in chlorine production.
Pesticides:
K031 NA9354 Byproduct salts generated in the production of MSMA and cacodylic acid.
K032 NA9355 Wastewater treatment sludge from the production of chlordane.
K033 NA9356 Wastewater and scrub water from the chlorination of cyclopentadiene in the production of chlordane.
K034 NA9357 Filter solids from the filtration of hexachlorocyclopentadiene in the production of chlordane.
K035 NA9359 Wastewater treatment sludges generated in the production of creosote.
K036 NA9360 Still bottoms from toluene reclamation distillation in the production of disulphoton.
K037 NA9361 Wastewater treatment sludges from the production of disulphoton.
K038 NA9362 Wastewater from the washing and stripping of phorate production.
K039 NA9363 Filter cake from the filtration of diethyl phosphorodithioic acid in the production of phorate.
K040 NA9364 Wastewater treatment sludge from the production of phorate.
K041 NA9365 Wastewater treatment sludge from the production of toxaphene.
K042 NA9367 Heavy ends or distillation residues from the distillation of tetrachlorobenzene in the production of 2,4,5T.
K043 NA9368 2,6 Dichlorophenol waste from the production of 2,4D.
K097 NA9358 Vacuum stripper discharge from the chlordane chlorinator in the production of chlordane.
K098 NA9366 Untreated process wastewater from the production of toxaphene.
K099 NA9369 Untreated wastewater from the production of 2,4D.
K123 Process wastewater (including supernates, filtrates, and washwaters) from the production of ethylenebisdithiocarbamic acid and its salt.
K124 Reactor vent scrubber water from the production of ethylenebisdithiocarbamic acid and its salts.
K125 Filtration, evaporation, and centrifugation solids from the production of ethylenebisdithiocarbamic acid and its salts.
K126 Baghouse dust and floor sweepings in milling and packaging operations from the production or formulation of ethylenebisdithiocarbamic acid and its salts.
K131 Wastewater from the reactor and spent sulfuric acid from the acid dryer from the production of methyl bromide.
K132 Spent absorbent and wastewater separator solids from the production of methyl bromide.
Explosives:
K044 NA9370 Wastewater treatment sludges from the manufacturing and processing of explosives.
K045 NA9371 Spent carbon from the treatment of wastewater containing explosives.
K046 NA9372 Wastewater treatment sludges from the manufacturing formulation and loading of leadbased initiating compounds.
K047 NA9373 Pink/red water from TNT operations.
Petroleum refining:
K048 NA9374 Dissolved air flotation (DAF) float from the petroleum refining industry.
K049 NA9375 Slop oil emulsion solids from the petroleum refining industry.
K050 NA9376 Heat exchanger bundle cleaning sludge from the petroleum refining industry.
K051 NA9377 API separator sludge from the petroleum refining industry.
K052 NA9378 Tank bottoms (leaded) from the petroleum refining industry.
K169 Crude oil storage tank sediment from petroleum refining operations.
K170 Clarified slurry oil tank sediment and/or in-line filter/separation solids from petroleum refining operations.
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).
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).
Iron and steel:
K061 NA9380 Emission control dust/sludge from the primary production of steel in electric furnaces.
K062 NA9381 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.
Primary copper:
K064 NA9383 Acid plant blowdown slurry/sludge resulting from the thickening of blowdown slurry from primary copper production.
Primary lead:
K065 NA9384 Surface impoundment solids contained in and dredged from surface impoundments at primary lead smelting facilities.
Primary zinc:
K066 NA9385 Sludge from treatment of process wastewater and/or acid plant blowdown from primary zinc production.
Primary aluminum:
K088 Spent potliners from primary aluminum reduction.
Ferroalloys:
K090 Emission control dust or sludge from ferrochromiumsilicon production.
K091 Emission control dust or sludge from ferrochromium production.
Secondary lead:
K069 NA9388 Emission control dust/sludge from secondary lead smelting. (NOTE: This listing is stayed administratively for sludge generated from secondary acid scrubber systems. The stay will remain in effect until further administrative action is taken. If EPA takes further action effecting this stay, EPA will publish a notice of the action in the Federal Register.
K100 NA9389 Waste leaching solution from acid leaching of emission control dust/sludge from secondary lead smelting.
Veterinary pharmaceuticals:
K084 NA9394 Wastewater treatment sludges generated during the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.
K101 NA9395 Distillation tar residues from the distillation of anilinebased compounds in the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.
K102 NA9396 Residue from the use of activated carbon for decolourization in the production of veterinary pharmaceuticals from arsenic or organoarsenic compounds.
Ink formulation:
K086 NA9393 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.
Coking:
K060 NA9379 Ammonia still lime sludge from coking operations.
K087 NA9397 Decanter tank tar sludge from coking operations.
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).
K142 Tar storage tank residues from the production of coke from coal or from the recovery of coke by-products produced from coal.
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.
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.
K145 Residues from naphthalene collection and recovery operations from the recovery of coke by-products produced from coal.
K147 Tar storage tank residues from coal tar refining.
K148 Residues from coal tar distillation, including but not limited to, still bottoms.

1 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

[O. Reg. 240/92, s. 2; 507/93, s. 1; 558/00, s. 4]

Schedule 1.1 EXEMPT HAZARDOUS INDUSTRIAL WASTES

Exempt Hazardous Industrial Wastes

Industry and Site Waste
ICI Canada Inc, Cornwall Brine purification muds (known either as K071 or No. NA9390, 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 (known either as K062 or No. NA9381) 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 (known also as No. NA9380) or K062 ( known also as No. NA9381) 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 (known also as No. NA9306) 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. 240/92, s. 3; 460/99, s. 7; 558/00, s. 4]

Schedule 2

Part A - Acute Hazardous Waste Chemicals

Hazardous Waste No. Chemical Abstracts No. Substance Reference Number
P026 5344-82-1 1-(o-Chlorophenyl)thiourea ON1037
P081 55-63-0 1,2,3-Propanetriol, trinitrate ON1089
P042 51-43-4 1,2-Benzenediol,4-[1-hydroxy-2-(meth ylamino)ethyl]- ON1025
P067 75-55-8 1,2-Propylenimine ON1082
P185 26419-73-8 1,3-Dithiolane-2-carboxaldehyde, 2,4-dimethyl-, O-[(methylamino)-carbonyl] oxime
P004 309-00-2 1,4,5,8 -Dimethano naphthalene,1,2,3,4,10,10-hexa-chloro- 1,4,4a,5,8,8a,-hexahydro-,(1alpha, 4alpha, 4abeta, 5alpha,8alpha,8abeta) ON1010
P060 465-73-6 1 ,4,5,8-Dimethanonaphthalene,1,2,3,4,1 0,10-hexa-chloro-1,4,4a,5,8,8a- hexahydro-, (1alpha,4alpha, 4abeta, 5beta, 8beta, 8abeta)- ON1070
P002 591-08-2 1-Acetyl-2-thiourea ON1002
P048 51-28-5 2,4-Dinitrophenol ON1055
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 ON1062
P037 60-57-1 2,7:3,6-Dimet hanonaphth[2,3-b]oxirene,3,4,5,6,9,9-h exachloro-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- ON1043
P045 39196-18-4 2-Butanone,3,3-dimethyl-1-methylthio) -,O-[methylamino)carbonyl] oxime ON1049
P034 131-89-5 2-Cyclohexyl-4,6-dinitrophenol ON1054
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% ON1006
P069 75-86-5 2-Methyllactonitrile ON1005
P017 598-31-2 2-Propanone, 1-bromo- ON1029
P005 107-18-6 2-Propen-1-ol ON1011
P003 107-02-8 2-Propenal ON1007
P102 107-19-7 2-Propyn-1-ol ON1097
P007 2763-96-4 3(2H)-Isoxazolone, 5-(aminomethyl)- ON1008
P027 542-76-7 3-Chloropropionitrile ON1038
P202 64-00-6 3-Isopropylphenyl N-methylcarbamate
P047 ** 534-52-1 4,6-Dinitro-o-cresol, & salts ON1053
P059 76-44-8 4,7-Methano-1H-indene, 1,4,5,6,7,8,8- heptachloro-3a,4,7,7a-tetrahydro- ON1069
P008 504-24-5 4-Aminopyridine ON1013
P008 504-24-5 4-Pyridinamine ON1013
P007 2763-96-4 5-(Aminomethyl)-3-isoxazolol ON1008
P050 115-29-7 6,9-Methano-2, 4,3-benzodioxathiepin,6,7,8,9,10,10-he xachloro-1,5,5a,6,9,9a-hexahydro-,3- oxide ON1060
P127 1563-66-2 7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-, methylcarbamate
P088 145-73-3 7-Oxabicyclo[2.2.1]heptane-2,3-dicarb oxylic acid ON1061
P023 107-20-0 Acetaldehyde, chloro- ON1001
P057 640-19-7 Acetamide, 2-fluoro- ON1003
P002 591-08-2 Acetamide, N-(aminothioxomethyl)- ON1002
P058 62-74-8 Acetic acid, fluoro-, sodium salt ON1067
P003 107-02-8 Acrolein ON1007
P070 116-06-3 Aldicarb ON1009
P203 1646-88-4 Aldicarb sulfone
P004 309-00-2 Aldrin ON1010
P005 107-18-6 Allyl alcohol ON1011
P046 122-09-8 alpha,alpha-Dimethylphenethylamine ON1052
P072 86-88-4 alpha-Naphthylthiourea ON1083
P006 20859-73-8 Aluminum phosphide ON1012
P009 131-74-8 Ammonium picrate ON1015
P119 7803-55-6 Ammonium vanadate ON1014
P099 506-61-6 Argentate(1-), bis(cyano-C)-, potassium ON1096
P010 7778-39-4 Arsenic acid H 3 AsO 4 ON1016
P012 1327-53-3 Arsenic oxide As 2 O 3 ON1017
P011 1303-28-2 Arsenic oxide As 2 O 5 ON1018
P011 1303-28-2 Arsenic pentoxide ON1018
P012 1327-53-3 Arsenic trioxide ON1017
P038 692-42-2 Arsine, diethyl- ON1019
P036 696-28-6 Arsonous dichloride, phenyl- ON1042
P054 151-56-4 Aziridine ON1020
P067 75-55-8 Aziridine, 2-methyl- ON1082
P013 542-62-1 Barium cyanide ON1021
P024 106-47-8 Benzenamine,4-chloro- ON1022
P077 100-01-6 Benzenamine, 4-nitro- ON1023
P028 100-44-7 Benzene, (chloromethyl)- ON1024
P046 122-09-8 Benzeneethanamine, alpha,alpha-dimethyl- ON1052
P014 108-98-5 Benzenethiol ON1026
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)
P028 100-44-7 Benzyl chloride ON1024
P015 7440-41-7 Beryllium powder ON1027
P017 598-31-2 Bromoacetone ON1029
P018 357-57-3 Brucine ON1030
P021 592-01-8 Calcium cyanide ON1031
P021 592-01-8 Calcium cyanide Ca(CN) 2 ON1031
P189 55285-14-8 Carbamic acid, [(dibutylamino)-thio]methyl-, 2,3-dihydro-2,2-dimethyl- 7-benzofuranyl ester
P191 644-64-4 Carbamic acid, dimethyl-, 1-[(dimethyl-amino)carbonyl]- 5-methyl-1H- pyrazol-3-yl este
P190 1129-41-5 Carbamic acid, methyl-, 3-methylphenyl ester
P192 119-38-0 Carbamic acid,dimethyl-,3-methyl-1-(1methyleth yl)-1H-pyrazol-5-yl ester
P127 1563-66-2 Carbofuran
P022 75-15-0 Carbon disulfide ON1034
P095 75-44-5 Carbonic dichloride ON1035
P189 55285-14-8 Carbosulfan
P023 107-20-0 Chloroacetaldehyde ON1001
P029 544-92-3 Copper cyanide ON1039
P029 544-92-3 Copper cyanide Cu(CN) ON1039
P030 N/A Cyanides (soluble cyanide salts), not otherwise specified ON1040
P031 460-19-5 Cyanogen ON1041
P033 506-77-4 Cyanogen chloride ON1036
P033 506-77-4 Cyanogen chloride (CN)Cl ON1036
P016 542-88-1 Dichloromethyl ether ON1028
P036 696-28-6 Dichlorophenylarsine ON1042
P037 60-57-1 Dieldrin ON1043
P038 692-42-2 Diethylarsine ON1019
P041 311-45-5 Diethyl-p-nitrophenyl phosphate ON1045
P043 55-91-4 Diisopropylfluorophosphate (DFP) ON1047
P044 60-51-5 Dimethoate ON1048
P191 644-64-4 Dimetilan.
P020 88-85-7 Dinoseb ON1056
P085 152-16-9 Diphosphoramide, octamethyl- ON1057
P111 107-49-3 Diphosphoric acid, tetraethyl ester ON1098
P039 298-04-4 Disulfoton ON1044
P049 541-53-7 Dithiobiuret ON1058
P050 115-29-7 Endosulfan ON1060
P088 145-73-3 Endothall ON1061
P051 72-20-8 Endrin ON1062
P051 72-20-8 Endrin, & metabolites ON1062
P042 51-43-4 Epinephrine ON1025
P031 460-19-5 Ethanedinitrile ON1041
P194 23135-22-0 Ethanimidothioc acid, 2-(dimethylamino)-N-[[(methylamino) carbonyl]oxy]-2- oxo-, methyl ester
P066 16752-77-5 Ethanimidothioic acid, N-[[(methylamino)carbonyl]oxy]-,meth yl ester ON1004
P101 107-12-0 Ethyl cyanide ON1064
P054 151-56-4 Ethyleneimine ON1020

Part A - Acute Hazardous Waste Chemicals...cont'd

Hazardous Waste No. Chemical Abstracts No. Substance Reference Number
P097 52-85-7 Famphur ON1065
P056 7782-41-4 Fluorine ON1066
P057 640-19-7 Fluoroacetamide ON1003
P058 62-74-8 Fluoroacetic acid, sodium salt ON1067
P198 23422-53-9 Formetanate hydrochloride
P197 17702-57-7 Formparanate
P065 628-86-4 Fulminic acid, mercury(2+) salt ON1068
P059 76-44-8 Heptachlor ON1069
P062 757-58-4 Hexaethyl tetraphosphate ON1072
P068 60-34-4 Hydrazine, methyl- ON1074
P116 79-19-6 Hydrazinecarbothioamide ON1073
P063 74-90-8 Hydrocyanic acid ON1075
P063 74-90-8 Hydrogen cyanide ON1075
P096 7803-51-2 Hydrogen phosphide ON1077
P060 465-73-6 Isodrin ON1070
P192 119-38-0 Isolan
P196 15339-36-3 Manganese dimethyl dithiocarbamate
P196 15339-36-3 Manganese,bis(dimethylcarbamodithio ato-S,S')-
P202 64-00-6 M-Cumenyl methylcarbamate
P065 628-86-4 Mercury fulminate ON1068
P092 62-38-4 Mercury, (acetato-O)phenyl- ON1079
P082 62-75-9 Methanamine, N-methyl-N-nitroso- ON1051
P064 624-83-9 Methane, isocyanato- ON1078
P016 542-88-1 Methane, oxybis[chloro- ON1028
P112 509-14-8 Methane, tetranitro- ON1080
P118 75-70-7 Methanethiol, trichloro- ON1081
P197 17702-57-7 Methanimidamide,N,N-dimethyl-N'-[2-m ethyl-4-[[(methylamino)carbonyl]oxy] phenyl]-
P198 23422-53-9 Methanimidamide,N,N-dimethyl-N'-[3- [[(methylamino)-carbonyl]oxy]phenyl] -, monohydrochloride
P199 2032-65-7 Methiocarb
P066 16752-77-5 Methomyl ON1004
P068 60-34-4 Methyl hydrazine ON1074
P064 624-83-9 Methyl isocyanate ON1078
P071 298-00-0 Methyl parathion ON1050
P190 1129-41-5 Metolcarb
P128 315-8-4 Mexacarbate
P073 13463-39-3 Nickel carbonyl ON1084
P073 13463-39-3 Nickel carbonyl Ni(CO) 4 ,(T-4)- ON1084
P074 557-19-7 Nickel cyanide ON1085
P074 557-19-7 Nickel cyanide Ni(CN) 2 ON1085
P075 ** 54-11-5 Nicotine, & salts ON1086
P076 10102-43-9 Nitric oxide ON1087
P078 10102-44-0 Nitrogen dioxide ON1088
P076 10102-43-9 Nitrogen oxide NO ON1087
P078 10102-44-0 Nitrogen oxide NO 2 ON1088
P081 55-63-0 Nitroglycerine ON1089
P082 62-75-9 N-Nitrosodimethylamine ON1051
P084 4549-40-0 N-Nitrosomethylvinylamine ON1063
P040 297-97-2 O,O-Diethyl O-pyrazinyl phosphorothioate ON1046
P085 152-16-9 Octamethylpyrophosphoramide ON1057
P087 20816-12-0 Osmium oxide OsO 4 ,(T-4)- ON1090
P087 20816-12-0 Osmium tetroxide ON1090
P194 23135-22-0 Oxamyl
P089 56-38-2 Parathion ON1091
P024 106-47-8 p-Chloroaniline ON1022
P020 88-85-7 Phenol, 2-(1-methylpropyl)-4,6-dinitro- ON1056
P009 131-74-8 Phenol, 2,4,6-trinitro-, ammonium salt ON1015
P048 51-28-5 Phenol, 2,4-dinitro- ON1055
P034 131-89-5 Phenol, 2-cyclohexyl-4,6-dinitro- ON1054
P047 ** 534-52-1 Phenol, 2-methyl-4,6-dinitro-, & salts ON1053
P202 64-00-6 Phenol, 3-(1-methylethyl)-, methyl carbamate
P201 2631-37-0 Phenol, 3-methyl-5-(1-methylethyl)-,methyl carbamate
P199 2032-65-7 Phenol,(3,5-dimethyl-4-(methylthio)-, methylcarbamate
P128 315-18-4 Phenol,4-(dimethylamino)-3,5-dimethy l-, methylcarbamate (ester)
P092 62-38-4 Phenylmercury acetate ON1079
P093 103-85-5 Phenylthiourea ON1092
P094 298-02-2 Phorate ON1093
P095 75-44-5 Phosgene ON1035
P096 7803-51-2 Phosphine ON1077
P041 311-45-5 Phosphoric acid, diethyl 4-nitrophenyl ester ON1045
P094 298-02-2 Phosphorodithioic acid, O,O-diethyl S-[(ethylthio)methyl] ester ON1093
P039 298-04-4 Phosphorodithioic acid, O,O-diethyl S-[2-(ethylthio)ethyl] ester ON1044
P044 60-51-5 Phosphorodithioic acid,O,O-dimethylS-[2-(methylamino)- 2-oxoethyl] ester ON1048
P043 55-91-4 Phosphorofluoridic acid, bis(1-methylethyl) ester ON1047
P071 298-00-0 Phosphorothioic acid, O,O,-dimethyl O-(4-nitrophenyl) ester ON1050
P089 56-38-2 Phosphorothioic acid, O,O-diethyl O-(4-nitrophenyl) ester ON1091
P040 297-97-2 Phosphorothioic acid, O,O-diethyl O-pyrazinyl ester ON1046
P097 52-85-7 Phosphorothioic acid, O-[4-[(dimethylamino)sulfonyl]phenyl] O,O-r dimethyl ester ON1065
P188 57-64-7 Physostigmine salicylate.
P204 57-47-6 Physostigmine.
P110 78-00-2 Plumbane, tetraethyl- ON1094
P077 100-01-6 p-Nitroaniline ON1023
P098 151-50-8 Potassium cyanide ON1095
P098 151-50-8 Potassium cyanide K(CN) ON1095
P099 506-61-6 Potassium silver cyanide ON1096
P201 2631-37-0 Promecarb
P203 1646-88-4 Propanal,2-methyl-2-(methyl-sulfonyl)- ,O-[(methylamino)carbonyl] oxime
P070 116-06-3 Propanal,2-methyl-2-(methylthio)-,O-[( methylamino)carbonyl]oxime ON1009
P101 107-12-0 Propanenitrile ON1064
P069 75-86-5 Propanenitrile, 2-hydroxy-2-methyl- ON1005
P027 542-76-7 Propanenitrile, 3-chloro- ON1038
P102 107-19-7 Propargyl alcohol ON1097
P075 ** 54-11-5 Pyridine, 3-(1-methyl-2-pyrrolidinyl)-, (S)-, & salts ON1086
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)-
P114 12039-52-0 Selenious acid, dithallium(1+) salt ON1106
P103 630-10-4 Selenourea ON1033
P104 506-64-9 Silver cyanide ON1099
P104 506-64-9 Silver cyanide Ag(CN) ON1099
P105 26628-22-8 Sodium azide ON1100
P106 143-33-9 Sodium cyanide ON1101
P106 143-33-9 Sodium cyanide Na(CN) ON1101
P108 ** 57-24-9 Strychnidin-10-one, & salts ON1103
P018 357-57-3 Strychnidin-10-one, 2,3-dimethoxy- ON1030
P108 ** 57-24-9 Strychnine, & salts ON1103

Part A - Acute Hazardous Waste Chemicals...cont'd

Hazardous Waste No. Chemical Abstracts No. Substance Reference Number
P115 7446-18-6 Sulfuric acid, dithallium(1+) salt ON1105
P110 78-00-2 Tetraethyl lead ON1094
P111 107-49-3 Tetraethyl pyrophosphate ON1098
P109 3689-24-5 Tetraethyldithiopyrophosphate ON1059
P112 509-14-8 Tetranitromethane ON1080
P062 757-58-4 Tetraphosphoric acid, hexaethyl ester ON1072
P113 1314-32-5 Thallic oxide ON1104
P113 1314-32-5 Thallium oxide Tl 2 O 3 ON1104
P114 12039-52-0 Thallium(I) selenite ON1106
P115 7446-18-6 Thallium(I) sulfate ON1105
P109 3689-24-5 Thiodiphosphoric acid, tetraethyl ester ON1059
P045 39196-18-4 Thiofanox ON1049
P049 541-53-7 Thioimidodicarbonic diamide [(H 2 N)C(S)] 2 NH ON1058
P014 108-98-5 Thiophenol ON1026
P116 79-19-6 Thiosemicarbazide ON1073
P026 5344-82-1 Thiourea, (2-chlorophenyl)- ON1037
P072 86-88-4 Thiourea, 1-naphthalenyl- ON1083
P093 103-85-5 Thiourea, phenyl- ON1092
P185 26419-73-8 Tirpate
P123 8001-35-2 Toxaphene ON1032
P118 75-70-7 Trichloromethanethiol ON1081
P119 7803-55-6 Vanadic acid, ammonium salt ON1014
P120 1314-62-1 Vanadium oxide V 2 O 5 ON1107
P120 1314-62-1 Vanadium pentoxide ON1107
P084 4549-40-0 Vinylamine, N-methyl-N-nitroso- ON1063
P001 ** 81-81-2 Warfarin, & salts, when present at concentrations greater than 0.3% ON1006
P121 557-21-1 Zinc cyanide ON1108
P121 557-21-1 Zinc cyanide Zn(CN) 2 ON1108
P122 1314-84-7 Zinc phosphide Zn 3 P 2 , when present at concentrations greater than 10% ON1109
P205 137-30-4 Zinc, bis(dimethylcarbamodithioato-S,S')-,
P205 137-30-4 Ziram

Part B - Hazardous Waste Chemicals

Hazardous Waste No. Chemical Abstracts No. Substance Reference Number
U021 92-87-5 [1,1-Biphenyl]-4,4-diamine ON2064
U073 91-94-1 [1,1'-Biphenyl]-4,4'-diamine, 3,3'-dichloro- ON2071
U091 119-90-4 [1,1'-Biphenyl]-4,4'-diamine, 3,3'-dimethoxy- ON2072
U095 119-93-7 [1,1'-Biphenyl]-4,4'-diamine, 3,3'-dimethyl- ON2073
U208 630-20-6 1,1,1,2-Tetrachloroethane ON2158
U209 79-34-5 1,1,2,2-Tetrachloroethane ON2159
U227 79-00-5 1,1,2-Trichloroethane ON2162
U078 75-35-4 1,1-Dichloroethylene ON2128
U098 57-14-7 1,1-Dimethylhydrazine ON2144
U207 95-94-3 1,2,4,5-Tetrachlorobenzene ON2061
U085 1464-53-5 1,2:3,4-Diepoxybutane ON2070
U069 84-74-2 1,2-Benzenedicarboxylic acid, dibutyl ester ON2037
U088 84-66-2 1,2-Benzenedicarboxylic acid, diethyl ester ON2038
U102 131-11-3 1,2-Benzenedicarboxylic acid, dimethyl ester ON2039
U107 117-84-0 1,2-Benzenedicarboxylic acid, dioctyl ester ON2040
U028 117-81-7 1,2-Benzenedicarboxylic acid,bis(2-ethylhexyl) ester ON2036
U202 ** 81-07-2 1,2-Benzisothiazol-3(2H)-one, 1,1-dioxide, & salts ON2065
U066 96-12-8 1,2-Dibromo-3-chloropropane ON2124
U079 156-60-5 1,2-Dichloroethylene ON2129
U099 540-73-8 1,2-Dimethylhydrazine ON2145
U109 122-66-7 1,2-Diphenylhydrazine ON2148
U155 91-80-5 1,2-Ethanediamine,N,N-dimethyl-N'-2- pyridinyl-N'-(2-thienylmethyl)- ON2202
U193 1120-71-4 1,2-Oxathiolane, 2,2-dioxide ON2216
U142 143-50-0 1,3,4-Metheno-2H-cyclobuta[cd]pental en-2-one, 1,1a,3,3a,4,5,5,5a,5b,6-decachloroocta hydro- ON2118
U234 99-35-4 1,3,5-Trinitrobenzene ON2063
U182 123-63-7 1,3,5-Trioxane, 2,4,6-trimethyl- ON2217
U201 108-46-3 1,3-Benzenediol ON2046
U364 22961-82-6 1,3-Benzodioxol-4-ol, 2,2-dimethyl-,
U278 22781-23-3 1,3-Benzodioxol-4-ol, 2,2-dimethyl-,methyl carbamate
U141 120-58-1 1,3-Benzodioxole, 5-(1-propenyl)- ON2054
U203 94-59-7 1,3-Benzodioxole, 5-(2-propenyl)- ON2053
U090 94-58-6 1,3-Benzodioxole, 5-propyl- ON2055
U128 87-68-3 1,3-Butadiene, 1,1,2,3,4,4-hexachloro- ON2079
U130 77-47-4 1,3-Cyclopentadiene, 1,2,3,4,5,5-hexachloro- ON2112
U084 542-75-6 1,3-Dichloropropene ON2135
U190 85-44-9 1,3-Isobenzofurandione ON2035
U186 504-60-9 1,3-Pentadiene ON2203
U193 1120-71-4 1,3-Propane sultone ON2216
U074 764-41-0 1,4-Dichloro-2-butene ON2086
U108 123-91-1 1,4-Diethyleneoxide ON2136
U108 123-91-1 1,4-Dioxane ON2136
U166 130-15-4 1,4-Naphthalenedione ON2208
U166 130-15-4 1,4-Naphthoquinone ON2208
U172 924-16-3 1-Butanamine, N-butyl-N-nitroso- ON2080
U031 71-36-3 1-Butanol ON2082
U011 61-82-5 1H-1,2,4-Triazol-3-amine ON2016
U186 504-60-9 1-Methylbutadiene ON2203
U167 134-32-7 1-Naphthalenamine ON2210
U279 63-25-2 1-Naphthalenol, methylcarbamate
U194 107-10-8 1-Propanamine ON2224
U111 621-64-7 1-Propanamine, N-nitroso-N-propyl- ON2150
U110 142-84-7 1-Propanamine, N-propyl- ON2149
U235 126-72-7 1-Propanol, 2,3-dibromo-, phosphate (3:1) ON2225
U140 78-83-1 1-Propanol, 2-methyl- ON2189
U243 1888-71-7 1-Propene, 1,1,2,3,3,3-hexachloro- ON2184
U084 542-75-6 1-Propene, 1,3-dichloro- ON2135
U085 1464-53-5 2,2-Bioxirane ON2070
F027 58-90-2 2,3,4,6-Tetrachlorophenol ON2219
U237 66-75-1 2,4-(1H,3H)-Pyrimidinedione, 5-[bis(2-chloroethyl)amino]- ON2237
F027 93-76-5 2,4,5-T ON2233
F027 95-95-4 2,4,5-Trichlorophenol ON2220
U408 118-79-6 2,4,6-Tribromophenol
F027 88-06-2 2,4,6-Trichlorophenol ON2221
U240 ** 94-75-7 2,4-D, salts & esters ON2114
U081 120-83-2 2,4-Dichlorophenol ON2132
U101 105-67-9 2,4-Dimethylphenol ON2146
U105 121-14-2 2,4-Dinitrotoluene ON2051
U197 106-51-4 2,5-Cyclohexadiene-1,4-dione ON2068
U147 108-31-6 2,5-Furandione ON2177
U082 87-65-0 2,6-Dichlorophenol ON2133
U106 606-20-2 2,6-Dinitrotoluene ON2052
U236 72-57-1 2,7-Naphthalenedisulfonic acid, 3,3'-[(3,3 '-dimethyl[1,1'-biphenyl]-4,4'-diyl)bis(a zo)bis[5-amino-4-hydroxy]-, tetrasodium salt ON2209
U005 53-96-3 2-Acetylaminofluorene ON2004
U159 78-93-3 2-Butanone ON2083

Part B - Hazardous Waste Chemicals...cont'd

Hazardous Waste No. Chemical Abstracts No. Substance Reference Number
U160 1338-23-4 2-Butanone, peroxide ON2084
U053 4170-30-3 2-Butenal ON2085
U074 764-41-0 2-Butene, 1,4-dichloro- ON2086
U143 303-34-4 2-Butenoic acid, 2-methyl-, 7-[[2,3- dihy droxy-2-(1-me thoxyethyl)-3-methyl-1-oxobutoxy]met hyl]-2,3,5,7a-tetrahydro-1H-pyrrolizin- 1-yl ester,[1S-[1alpha(Z),7(2S*,3R*), 7aalpha]]- ON2190
U042 110-75-8 2-Chloroethyl vinyl ether ON2103
U125 98-01-1 2-Furancarboxaldehyde ON2176
U058 50-18-0 2H-1,3,2-Oxazaphosphorin-2-amine,N, N-bis(2-chloroethyl)tetrahydro-, 2- oxide ON2113
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 ON2009
U116 96-45-7 2-Imidazolidinethione ON2169
U168 91-59-8 2-Naphthalenamine ON2211
U171 79-46-9 2-Nitropropane ON2213
U191 109-06-8 2-Picoline ON2223
U002 67-64-1 2-Propanone ON2226
U007 79-06-1 2-Propenamide ON2012
U009 107-13-1 2-Propenenitrile ON2014
U152 126-98-7 2-Propenenitrile, 2-methyl- ON2195
U008 79-10-7 2-Propenoic acid ON2013
U118 97-63-2 2-Propenoic acid, 2-methyl-, ethyl ester ON2170
U162 80-62-6 2-Propenoic acid, 2-methyl-, methyl ester ON2205
U113 140-88-5 2-Propenoic acid, ethyl ester ON2167
U073 91-94-1 3,3'-Dichlorobenzidine ON2071
U091 119-90-4 3,3'-Dimethoxybenzidine ON2072
U095 119-93-7 3,3'-Dimethylbenzidine ON2073
U148 123-33-1 3,6-Pyridazinedione, 1,2-dihydro- ON2141
U157 56-49-5 3-Methylcholanthrene ON2021
U164 56-04-2 4(1H)-Pyrimidinone, 2,3-dihydro-6-methyl-2-thioxo- ON2206
U158 101-14-4 4,4'-Methylenebis(2-chloroaniline) ON2028
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- ON2099
U030 101-55-3 4-Bromophenyl phenyl ether ON2033
U049 3165-93-3 4-Chloro-o-toluidine, hydrochloride ON2026
U161 108-10-1 4-Methyl-2-pentanone ON2204
U059 20830-81-3 5,12-Naphthacenedione ,8-acetyl-10-[(3-amino-2,3,6-trideoxy)- al pha-L-lyxo-hexopyranosyl)oxy]-7,8,9,1 0-tetrahydro-6,8,11-trihydroxy-1- methoxy-, (8S-cis)- ON2115
U181 99-55-8 5-Nitro-o-toluidine ON2030
U094 57-97-6 7,12-Dimethylbenz[a]anthracene ON2025
U367 1563-38-8 7-Benzofuranol, 2,3-dihydro-2,2-dimethyl-
U394 30558-43-1 A2213
U001 75-07-0 Acetaldehyde ON2001
U034 75-87-6 Acetaldehyde, trichloro- ON2002
U187 62-44-2 Acetamide, N-(4-ethoxyphenyl)- ON2003
U005 53-96-3 Acetamide, N-9H-fluoren-2-yl- ON2004
U112 141-78-6 Acetic acid ethyl ester ON2005
See F027 93-76-5 Acetic acid, (2,4,5-trichlorophenoxy)- ON2233
U240 ** 94-75-7 Acetic acid, (2,4-dichlorophenoxy)-,salts & esters ON2114
U144 301-04-2 Acetic acid, lead(2+) salt ON2006
U214 563-68-8 Acetic acid, thallium(1+) salt ON2007
U002 67-64-1 Acetone ON2226
U003 75-05-8 Acetonitrile ON2008
U004 98-86-2 Acetophenone ON2010
U006 75-36-5 Acetyl chloride ON2011
U007 79-06-1 Acrylamide ON2012
U008 79-10-7 Acrylic acid ON2013
U009 107-13-1 Acrylonitrile ON2014
U096 80-15-9 alpha,alpha-Dimethylbenzylhydroperoxide ON2143
U167 134-32-7 alpha-Naphthylamine ON2210
U011 61-82-5 Amitrole ON2016
U012 62-53-3 Aniline ON2017
U136 75-60-5 Arsinic acid, dimethyl- ON2087
U014 492-80-8 Auramine ON2018
U015 115-02-6 Azaserine ON2019
U010 50-07-7 Azirino[2,3_3,4]pyrro lo[1,2-a]indole-4,7-dione,6-amin o-8-[[(aminocarbonyl)oxy]methyl]-1,1 a,2,8,8a,8b-hexahydro-8a-methoxy-5- methyl-, [1aS-(1aalpha,8beta,8aalpha,8balpha)]- ON2020
U280 101-27-9 Barban.
U364 22961-82-6 Bendiocarb phenol
U278 22781-23-3 Bendiocarb.
U271 17804-35-2 Benomyl.
U018 56-55-3 Benz[a]anthracene ON2024
U094 57-97-6 Benz[a]anthracene, 7,12-dimethyl- ON2025
U016 225-51-4 Benz[c]acridine ON2022
U157 56-49-5 Benz[j]aceanthrylene, 1,2-dihydro-3-methyl- ON2021
U017 98-87-3 Benzal chloride ON2023
U192 23950-58-5 Benzamide,3,5-dichloro-N-(1,1-dimeth yl-2-propynyl)- ON2127
U012 62-53-3 Benzenamine ON2017
U328 95-53-4 Benzenamine, 2-methyl-
U222 636-21-5 Benzenamine, 2-methyl-, hydrochloride ON2029
U181 99-55-8 Benzenamine, 2-methyl-5-nitro- ON2030
U014 492-80-8 Benzenamine, 4,4-carbonimidoylbis[N,N-dimethyl- ON2018
U158 101-14-4 Benzenamine, 4,4-methylenebis[2-chloro- ON2028
U049 3165-93-3 Benzenamine, 4-chloro-2-methyl-,hydrochloride ON2026
U353 106-49-0 Benzenamine, 4-methyl-
U093 60-11-7 Benzenamine, N,N-dimethyl-4-(phenylazo)- ON2027
U019 71-43-2 Benzene ON2031
U055 98-82-8 Benzene, (1-methylethyl)- ON2056
U017 98-87-3 Benzene, (dichloromethyl)- ON2023
U023 98-07-7 Benzene, (trichloromethyl)- ON2062
U247 72-43-5 Benzene, 1,1-(2,2,2-trichloroethylidene)bis[4- methoxy- ON2163
U207 95-94-3 Benzene, 1,2,4,5-tetrachloro- ON2061
U070 95-50-1 Benzene, 1,2-dichloro- ON2041
U234 99-35-4 Benzene, 1,3,5-trinitro- ON2063
U071 541-73-1 Benzene, 1,3-dichloro- ON2042
U223 26471-62-5 Benzene, 1,3-diisocyanatomethyl- ON2044
U072 106-46-7 Benzene, 1,4-dichloro- ON2043
U030 101-55-3 Benzene, 1-bromo-4-phenoxy- ON2033
U105 121-14-2 Benzene, 1-methyl-2,4-dinitro- ON2051
U106 606-20-2 Benzene, 2-methyl-1,3-dinitro- ON2052
U037 108-90-7 Benzene, chloro- ON2034
U239 1330-20-7 Benzene, dimethyl- ON2045
U127 118-74-1 Benzene, hexachloro- ON2047
U056 110-82-7 Benzene, hexahydro- ON2048
U220 108-88-3 Benzene, methyl- ON2050
U169 98-95-3 Benzene, nitro- ON2057
U183 608-93-5 Benzene, pentachloro- ON2058
U185 82-68-8 Benzene, pentachloronitro- ON2059
U061 50-29-3 Benzene,1,1-(2,2,2-trichloroethylidene) bis[4-chloro- ON2117
U060 72-54-8 Benzene,1,1-(2,2-dichloroethylidene)bi s[4-chloro- ON2116
U038 510-15-6 Benzeneacetic acid,4-chloro-alpha- (4-chlorophenyl)-alpha-hydroxy-, ethyl ester ON2032
U035 305-03-3 Benzenebutanoic acid, 4-[bis(2-chloroethyl)amino]- ON2081
U221 25376-45-8 Benzenediamine, ar-methyl- ON2121
U020 98-09-9 Benzenesulfonic acid chloride ON2060
U020 98-09-9 Benzenesulfonyl chloride ON2060
U021 92-87-5 Benzidine ON2064

Part B - Hazardous Waste Chemicals...cont'd

Hazardous Waste No. Chemical Abstracts No. Substance Reference Number
U022 50-32-8 Benzo[a]pyrene ON2067
U064 189-55-9 Benzo[rst]pentaphene ON2123
U023 98-07-7 Benzotrichloride ON2062
U047 91-58-7 beta-Chloronaphthalene ON2106
U168 91-59-8 beta-Naphthylamine ON2211
U225 75-25-2 Bromoform ON2078
U136 75-60-5 Cacodylic acid ON2087
U032 13765-19-0 Calcium chromate ON2088
U280 101-27-9 Carbamic acid, (3-chlorophenyl)-, 4-chloro-2-butynyl ester
U409 23564-05-8 Carbamic acid, [1,2-phenylenebis (iminocarbonothioyl)]bis-, dimethyl ester
U271 17804-35-2 Carbamic acid, [1-[(butylamino)carbonyl]-1H-benzimi dazol-2-yl]-, methyl ester
U372 10605-21-7 Carbamic acid, 1H-benzimidazol-2-yl,methyl ester
U238 51-79-6 Carbamic acid, ethyl ester ON2089
U178 615-53-2 Carbamic acid, methylnitroso-, ethyl ester ON2090
U373 122-42-9 Carbamic acid, phenyl-, 1-methylethyl ester
U097 79-44-7 Carbamic chloride, dimethyl- ON2094
U114 ** 111-54-6 Carbamodithioic acid, 1,2-ethanediylbis-,salts & esters ON2155
U389 2303-17-5 Carbamothioic acid, bis(1-methylethyl)-, S-(2,3,3-trichloro-2-propenyl) ester
U062 2303-16-4 Carbamothioic acid, bis(1-methylethyl)-S-(2,3-dichloro-2-pr openyl) ester ON2119
U387 52888-80-9 Carbamothioic acid, dipropyl-, S-(phenylmethyl) ester
U279 63-25-2 Carbaryl
U372 10605-21-7 Carbendazim
U367 1563-38-8 Carbofuran phenol
U033 353-50-4 Carbon oxyfluoride ON2097
U211 56-23-5 Carbon tetrachloride ON2098
U215 6533-73-9 Carbonic acid, dithallium(1+) salt ON2095
U033 353-50-4 Carbonic difluoride ON2097
U156 79-22-1 Carbonochloridic acid, methyl ester ON2096
U034 75-87-6 Chloral ON2002
U035 305-03-3 Chlorambucil ON2081
U036 57-74-9 Chlordane, alpha & gamma isomers ON2099
U026 494-03-1 Chlornaphazin ON2100
U037 108-90-7 Chlorobenzene ON2034
U038 510-15-6 Chlorobenzilate ON2032
U044 67-66-3 Chloroform ON2104
U046 107-30-2 Chloromethyl methyl ether ON2105
U032 13765-19-0 Chromic acid H 2 CrO 4, calcium salt ON2088
U050 218-01-9 Chrysene ON2069
U051 N/A Creosote ON2108
U052 1319-77-3 Cresol (Cresylic acid) ON2109
U053 4170-30-3 Crotonaldehyde ON2085
U055 98-82-8 Cumene ON2056
U246 506-68-3 Cyanogen bromide (CN)Br ON2077
U056 110-82-7 Cyclohexane ON2048
U129 58-89-9 Cyclohexane, 1,2,3,4,5,6-hexachloro-,(1alpha,2alpha, 3beta,4alpha,5alpha,6 beta)- ON2182
U057 108-94-1 Cyclohexanone ON2111
U058 50-18-0 Cyclophosphamide ON2113
U059 20830-81-3 Daunomycin ON2115
U060 72-54-8 DDD ON2116
U061 50-29-3 DDT ON2117
U206 18883-66-4 D-Glucose,2-deoxy-2-[[(methylnitroso amino)-carbonyl]amino]- ON2179
U062 2303-16-4 Diallate ON2119
U063 53-70-3 Dibenz[a,h]anthracene ON2122
U064 189-55-9 Dibenzo[a,i]pyrene ON2123
U069 84-74-2 Dibutyl phthalate ON2037
U075 75-71-8 Dichlorodifluoromethane ON2126
U025 111-44-4 Dichloroethyl ether ON2130
U027 108-60-1 Dichloroisopropyl ether ON2075
U024 111-91-1 Dichloromethoxy ethane ON2074
U088 84-66-2 Diethyl phthalate ON2038
U395 5952-26-1 Diethylene glycol, dicarbamate
U028 117-81-7 Diethylhexyl phthalate ON2036
U089 56-53-1 Diethylstilbesterol ON2140
U090 94-58-6 Dihydrosafrole ON2055
U102 131-11-3 Dimethyl phthalate ON2039
U103 77-78-1 Dimethyl sulfate ON2147
U092 124-40-3 Dimethylamine ON2142
U097 79-44-7 Dimethylcarbamoyl chloride ON2094
U107 117-84-0 Di-n-octyl phthalate ON2040
U111 621-64-7 Di-n-propylnitrosamine ON2150
U110 142-84-7 Dipropylamine ON2149
U041 106-89-8 Epichlorohydrin ON2102
U001 75-07-0 Ethanal ON2001
U404 121-44-8 Ethanamine, N,N-diethyl-
U174 55-18-5 Ethanamine, N-ethyl-N-nitroso- ON2151
U208 630-20-6 Ethane, 1,1,1,2-tetrachloro- ON2158
U226 71-55-6 Ethane, 1,1,1-trichloro- ON2161
U209 79-34-5 Ethane, 1,1,2,2-tetrachloro- ON2159
U227 79-00-5 Ethane, 1,1,2-trichloro- ON2162
U024 111-91-1 Ethane, 1,1'-[methylenebis(oxy)]bis[2-chloro- ON2074
U076 75-34-3 Ethane, 1,1-dichloro- ON2153
U117 60-29-7 Ethane, 1,1'-oxybis- ON2137
U025 111-44-4 Ethane, 1,1'-oxybis[2-chloro- ON2130
U067 106-93-4 Ethane, 1,2-dibromo- ON2152
U077 107-06-2 Ethane, 1,2-dichloro- ON2154
U131 67-72-1 Ethane, hexachloro- ON2156
U184 76-01-7 Ethane, pentachloro- ON2157
U218 62-55-5 Ethanethioamide ON2160
U394 30558-43-1 Ethanimidothioic acid, 2-(dimethylamino)-N-hydroxy-2-oxo-, methyl ester
U410 59669-26-0 Ethanimidothioic acid, N,N'-[thiobis[(methylimino)carbonylox y]]bi s-, dimethyl ester
U173 1116-54-7 Ethanol, 2,2'-(nitrosoimino)bis- ON2164
U395 5952-26-1 Ethanol, 2,2'-oxybis-, dicarbamate
U359 110-80-5 Ethanol, 2-ethoxy- ON2239
U004 98-86-2 Ethanone, 1-phenyl- ON2010
U042 110-75-8 Ethene, (2-chloroethoxy)- ON2103
U078 75-35-4 Ethene, 1,1-dichloro- ON2128
U079 156-60-5 Ethene, 1,2-dichloro-, (E)- ON2129
U043 75-01-4 Ethene, chloro- ON2165
U210 127-18-4 Ethene, tetrachloro- ON2166
U228 79-01-6 Ethene, trichloro- ON2236
U112 141-78-6 Ethyl acetate ON2005
U113 140-88-5 Ethyl acrylate ON2167
U238 51-79-6 Ethyl carbamate (urethane) ON2089
U117 60-29-7 Ethyl ether ON2137
U118 97-63-2 Ethyl methacrylate ON2170
U119 62-50-0 Ethyl methanesulfonate ON2171
U067 106-93-4 Ethylene dibromide ON2152
U077 107-06-2 Ethylene dichloride ON2154
U359 110-80-5 Ethylene glycol monoethyl ether ON2239
U115 75-21-8 Ethylene oxide ON2168
U114 ** 111-54-6 Ethylenebisdithiocarbamic acid, salts & esters ON2155
U116 96-45-7 Ethylenethiourea ON2169
U076 75-34-3 Ethylidene dichloride ON2153
U120 206-44-0 Fluoranthene ON2066

Part B - Hazardous Waste Chemicals...cont'd

Hazardous Waste No. Chemical Abstracts No. Substance Reference Number
U122 50-00-0 Formaldehyde ON2173
U123 64-18-6 Formic acid ON2174
U124 110-00-9 Furan ON2175
U213 109-99-9 Furan, tetrahydro- ON2178
U125 98-01-1 Furfural ON2176
U124 110-00-9 Furfuran ON2175
U206 18883-66-4 Glucopyranose,2-deoxy-2-(3-methyl-3- nitrosoureido)-, D- ON2179
U126 765-34-4 Glycidylaldehyde ON2180
U163 70-25-7 Guanidine, N-methyl-N'-nitro-N-nitroso- ON2181
U127 118-74-1 Hexachlorobenzene ON2047
U128 87-68-3 Hexachlorobutadiene ON2079
U130 77-47-4 Hexachlorocyclopentadiene ON2112
U131 67-72-1 Hexachloroethane ON2156
U132 70-30-4 Hexachlorophene ON2183
U243 1888-71-7 Hexachloropropene ON2184
U133 302-01-2 Hydrazine ON2120
U098 57-14-7 Hydrazine, 1,1-dimethyl- ON2144
U086 1615-80-1 Hydrazine, 1,2-diethyl- ON2138
U099 540-73-8 Hydrazine, 1,2-dimethyl- ON2145
U109 122-66-7 Hydrazine, 1,2-diphenyl- ON2148
U134 7664-39-3 Hydrofluoric acid ON2185
U134 7664-39-3 Hydrogen fluoride ON2185
U135 7783-06-4 Hydrogen sulfide ON2187
U135 7783-06-4 Hydrogen sulfide H 2 S ON2187
U096 80-15-9 Hydroperoxide, 1-methyl-1-phenylethyl- ON2143
U137 193-39-5 Indeno[1,2,3-cd]pyrene ON2188
U140 78-83-1 Isobutyl alcohol ON2189
U141 120-58-1 Isosafrole ON2054
U142 143-50-0 Kepone ON2118
U143 303-34-4 Lasiocarpine ON2190
U144 301-04-2 Lead acetate ON2006
U145 7446-27-7 Lead phosphate ON2191
U146 1335-32-6 Lead subacetate ON2192
U146 1335-32-6 Lead, bis(acetato-O)tetrahydroxytri- ON2192
U129 58-89-9 Lindane ON2182
U150 148-82-3 L-Phenylalanine, 4-[bis(2-chloroethyl)amino]- ON2015
U015 115-02-6 L-Serine, diazoacetate (ester) ON2019
U147 108-31-6 Maleic anhydride ON2177
U148 123-33-1 Maleic hydrazide ON2141
U149 109-77-3 Malononitrile ON2193
U071 541-73-1 m-Dichlorobenzene ON2042
U150 148-82-3 Melphalan ON2015
U151 7439-97-6 Mercury ON2194
U152 126-98-7 Methacrylonitrile ON2195
U092 124-40-3 Methanamine, N-methyl- ON2142
U029 74-83-9 Methane, bromo- ON2196
U045 74-87-3 Methane, chloro- ON2197
U046 107-30-2 Methane, chloromethoxy- ON2105
U068 74-95-3 Methane, dibromo- ON2125
U080 75-09-2 Methane, dichloro- ON2131
U075 75-71-8 Methane, dichlorodifluoro- ON2126
U138 74-88-4 Methane, iodo- ON2198
U211 56-23-5 Methane, tetrachloro- ON2098
U225 75-25-2 Methane, tribromo- ON2078
U044 67-66-3 Methane, trichloro- ON2104
U121 75-69-4 Methane, trichlorofluoro- ON2200
U119 62-50-0 Methanesulfonic acid, ethyl ester ON2171
U153 74-93-1 Methanethiol ON2199
U154 67-56-1 Methanol ON2201
U155 91-80-5 Methapyrilene ON2202
U247 72-43-5 Methoxychlor ON2163
U154 67-56-1 Methyl alcohol ON2201
U029 74-83-9 Methyl bromide ON2196
U045 74-87-3 Methyl chloride ON2197
U156 79-22-1 Methyl chlorocarbonate ON2096
U226 71-55-6 Methyl chloroform ON2161
U159 78-93-3 Methyl ethyl ketone (MEK) ON2083
U160 1338-23-4 Methyl ethyl ketone peroxide ON2084
U138 74-88-4 Methyl iodide ON2198
U161 108-10-1 Methyl isobutyl ketone ON2204
U162 80-62-6 Methyl methacrylate ON2205
U068 74-95-3 Methylene bromide ON2125
U080 75-09-2 Methylene chloride ON2131
U164 56-04-2 Methylthiouracil ON2206
U010 50-07-7 Mitomycin C ON2020
U163 70-25-7 MNNG ON2181
U086 1615-80-1 N,N'-Diethylhydrazine ON2138
U026 494-03-1 Naphthalenamine, N,N'-bis(2-chloroethyl)- ON2100
U165 91-20-3 Naphthalene ON2207
U047 91-58-7 Naphthalene, 2-chloro- ON2106
U031 71-36-3 n-Butyl alcohol ON2082
U217 10102-45-1 Nitric acid, thallium(1+) salt ON2235
U169 98-95-3 Nitrobenzene ON2057
U173 1116-54-7 N-Nitrosodiethanolamine ON2164
U174 55-18-5 N-Nitrosodiethylamine ON2151
U172 924-16-3 N-Nitrosodi-n-butylamine ON2080
U176 759-73-9 N-Nitroso-N-ethylurea ON2091
U177 684-93-5 N-Nitroso-N-methylurea ON2092
U178 615-53-2 N-Nitroso-N-methylurethane ON2090
U179 100-75-4 N-Nitrosopiperidine ON2214
U180 930-55-2 N-Nitrosopyrrolidine ON2215
U194 107-10-8 n-Propylamine ON2224
U087 3288-58-2 O,O-Diethyl S-methyl dithiophosphate ON2139
U048 95-57-8 o-Chlorophenol ON2107
U070 95-50-1 o-Dichlorobenzene ON2041
U328 95-53-4 o-Toluidine
U222 636-21-5 o-Toluidine hydrochloride ON2029
U115 75-21-8 Oxirane ON2168
U041 106-89-8 Oxirane, (chloromethyl)- ON2102
U126 765-34-4 Oxiranecarboxyaldehyde ON2180
U182 123-63-7 Paraldehyde ON2217
U197 106-51-4 p-Benzoquinone ON2068
U039 59-50-7 p-Chloro-m-cresol ON2101
U072 106-46-7 p-Dichlorobenzene ON2043
U093 60-11-7 p-Dimethylaminoazobenzene ON2027
U183 608-93-5 Pentachlorobenzene ON2058
U184 76-01-7 Pentachloroethane ON2157
U185 82-68-8 Pentachloronitrobenzene (PCNB) ON2059
F027 87-86-5 Pentachlorophenol ON2218
U161 108-10-1 Pentanol, 4-methyl- ON2204
U187 62-44-2 Phenacetin ON2003
U188 108-95-2 Phenol ON2049
U411 114-26-1 Phenol, 2-(1-methylethoxy)-,methylcarbamate
F027 58-90-2 Phenol, 2,3,4,6-tetrachloro- ON2219

Part B - Hazardous Waste Chemicals...cont'd

Hazardous Waste No. Chemical Abstracts No. Substance Reference Number
F027 95-95-4 Phenol, 2,4,5-trichloro- ON2220
F027 88-06-2 Phenol, 2,4,6-trichloro- ON2221
U081 120-83-2 Phenol, 2,4-dichloro- ON2132
U101 105-67-9 Phenol, 2,4-dimethyl- ON2146
U082 87-65-0 Phenol, 2,6-dichloro- ON2133
U048 95-57-8 Phenol, 2-chloro- ON2107
U089 56-53-1 Phenol, 4,4'-(1,2-diethyl-1,2-ethenediyl)bis-, (E)- ON2140
U039 59-50-7 Phenol, 4-chloro-3-methyl- ON2101
U170 100-02-7 Phenol, 4-nitro- ON2212
U052 1319-77-3 Phenol, methyl- ON2109
F027 87-86-5 Phenol, pentachloro- ON2218
U132 70-30-4 Phenol,2,2'-methylenebis[3,4,6-trichlor o- ON2183
U145 7446-27-7 Phosphoric acid, lead(2+) salt (2:3) ON2191
U087 3288-58-2 Phosphorodithioic acid, O,O-diethyl S-methyl ester ON2139
U189 1314-80-3 Phosphorus sulfide ON2222
U190 85-44-9 Phthalic anhydride ON2035
U179 100-75-4 Piperidine, 1-nitroso- ON2214
U170 100-02-7 p-Nitrophenol ON2212
U192 23950-58-5 Pronamide ON2127
U066 96-12-8 Propane, 1,2-dibromo-3-chloro- ON2124
U083 78-87-5 Propane, 1,2-dichloro- ON2134
U027 108-60-1 Propane, 2,2'-oxybis[2-chloro- ON2075
U171 79-46-9 Propane, 2-nitro- ON2213
U149 109-77-3 Propanedinitrile ON2193
F027 93-72-1 Propanoic acid, 2-(2,4,5-0 trichlorophenoxy)- ON2227
U373 122-42-9 Propham
U411 114-26-1 Propoxur.
U083 78-87-5 Propylene dichloride ON2134
U387 52888-80-9 Prosulfocarb
U353 106-49-0 p-Toluidine
U196 110-86-1 Pyridine ON2228
U191 109-06-8 Pyridine, 2-methyl- ON2223
U180 930-55-2 Pyrrolidine, 1-nitroso- ON2215
U200 50-55-5 Reserpine ON2229
U201 108-46-3 Resorcinol ON2046
U202 ** 81-07-2 Saccharin, & salts ON2065
U203 94-59-7 Safrole ON2053
U204 7783-00-8 Selenious acid ON2230
U204 7783-00-8 Selenium dioxide ON2230
U205 7488-56-4 Selenium sulfide ON2232
U205 7488-56-4 Selenium sulfide SeS 2 ON2232
F027 93-72-1 Silvex (2,4,5-TP) ON2227
U206 18883-66-4 Streptozotocin ON2179
U189 1314-80-3 Sulfur phosphide ON2222
U103 77-78-1 Sulfuric acid, dimethyl ester ON2147
U210 127-18-4 Tetrachloroethylene ON2166
U213 109-99-9 Tetrahydrofuran ON2178
U216 7791-12-0 Thallium chloride TlCl ON2234
U214 563-68-8 Thallium(I) acetate ON2007
U215 6533-73-9 Thallium(I) carbonate ON2095
U216 7791-12-0 Thallium(I) chloride ON2234
U217 10102-45-1 Thallium(I) nitrate ON2235
U218 62-55-5 Thioacetamide ON2160
U410 59669-26-0 Thiodicarb
U153 74-93-1 Thiomethanol ON2199
U244 137-26-8 Thioperoxydicarbonic diamide[(H 2 N)C(S)] 2 S 2 , tetramethyl- ON2076
U409 23564-05-8 Thiophanate-methyl
U219 62-56-6 Thiourea ON2093
U244 137-26-8 Thiram ON2076
U220 108-88-3 Toluene ON2050
U223 26471-62-5 Toluene diisocyanate ON2044
U221 25376-45-8 Toluenediamine ON2121
U389 2303-17-5 Triallate
U228 79-01-6 Trichloroethylene ON2236
U121 75-69-4 Trichloromonofluoromethane ON2200
U404 121-44-8 Triethylamine
U235 126-72-7 Tris(2,3-dibromopropyl) phosphate ON2225
U236 72-57-1 Trypan blue ON2209
U237 66-75-1 Uracil mustard ON2237
U176 759-73-9 Urea, N-ethyl-N-nitroso- ON2091
U177 684-93-5 Urea, N-methyl-N-nitroso- ON2092
U043 75-01-4 Vinyl chloride ON2165
U248 ** 81-81-2 Warfarin, & salts, when present at concentrations of 0.3% or less ON2009
U239 1330-20-7 Xylene ON2045
U200 50-55-5 Yohimban-16-carboxylic acid,11,17-dimethoxy-18-[(3,4,5-trimet hoxybenzoyl)oxy]-,methyl ester,(3beta,16beta,17alpha, 18beta,20alpha)- ON2229
U249 1314-84-7 Zinc phosphide Zn 3 P 2 , when present at concentrations of 10% or less ON2238

** CAS number given for parent compound only

[O. Reg. 507/93, s. 2; 558/00, s. 4]

Schedule 2.1 EXEMPT ACUTE HAZARDOUS WASTE CHEMICALS

There are no wastes currently listed in this Schedule.

[O. Reg. 460/99, s. 8]

Schedule 2.2 EXEMPT HAZARDOUS WASTE CHEMICALS

There are no wastes currently listed in this Schedule.

[O. Reg. 460/99, s. 8]

Schedule 3 SEVERELY TOXIC CONTAMINANTS

Table

REFERENCE NUMBER CONTAMINANT
ON3001 Aflatoxin
ON3002 2,3,7,8-Tetrachlorodibenzo-p-dioxin
ON3003 1,2,3,7,8-Pentachlorodibenzo-p-dioxin
ON3004 1,2,3,4,7,8-Hexachlorodibenzo-p-dioxin
ON3005 1,2,3,6,7,8-Hexachlorodibenzo-p-dioxin
ON3006 1,2,3,7,8,9-Hexachlorodibenzo-p-dioxin
ON3007 2,3,7,8-Tetrachlorodibenzo furan

Schedule 4 LEACHATE QUALITY CRITERIA

Table

Contaminant Concentration (mg/l)
Aldicarb 0.9
Aldrin + Dieldrin 0.07
Arsenic 2.5
Atrazine + N-dealkylated metabolites (Weedex) 0.5
Azinphos-methyl 2.0
Barium 100.0
Bendiocarb 4.0
Benzene 0.5
Benzo(a)pyrene 0.001
Boron 500.0
Bromoxynil 0.5
Cadmium 0.5
Carbaryl/Sevin/1-Naphthyl-N methyl carbamate 9.0
Carbofuran 9.0
Carbon tetrachloride (Tetrachloromethane) 0.5
Chlordane 0.7
Chlorobenzene (Monochlorobenzene) 8.0
Chloroform 10.0
Chlorpyrifos 9.0
Chromium 5.0
Cresol (Mixture - total of all isomers, when isomers cannot be differentiated) 200.0
m-Cresol 200.0
o-Cresol 200.0
p-Cresol 200.0
Cyanazine 1.0
Cyanide 20.0
2,4-D / (2,4-dichlorophenoxy)acetic acid 10.0
2,4-DCP (2,4-Dichlorophenol) 90.0
DDT (total isomers) 3.0
Diazinon/Phosphordithioic acid, o,o-diethyl o-(2-isopropyl 6-methyl-4-pyrimidinyl) ester 2.0
Dicamba 12.0
1,2-Dichlorobenzene (o-Dichlorobenzene) 20.0
1,4-Dichlorobenzene (p-Dichlorobenzene) 0.5
1,2-Dichloroethane (Ethylene dichloride) 0.5
1,1-Dichloroethylene (Vinylidene chloride) 1.4
Dichloromethane (also see - methylene chloride) 5.0
Diclofop-methyl 0.9
Dimethoate 2.0
2,4-Dinitrotoluene 0.13
Dinoseb 1.0
Dioxin & Furan 0.0000015*
Diquat 7.0
Diuron 15.0
Endrin 0.02
Fluoride 150.0
Glyphosate 28.0
Heptachlor + Heptachlor epoxide 0.3
Hexachlorobenzene 0.13
Hexachlorobutadiene 0.5
Hexachloroethane 3.0
Lead 5.0
Lindane 0.4
Malathion 19.0
Mercury 0.1
Methoxychlor/1,1,1-Trichloro-2,2-bis(p-methoxyphenyl) ethane 90.0
Methyl ethyl ketone / Ethyl methyl ketone 200.0
Methyl Parathion 0.7
Methylene chloride / Dichloromethane 5.0
Metolachlor 5.0
Metribuzin 8.0
NDMA 0.0009
Nitrate + Nitrite (as Nitrogen) 1,000.0
Nitrilotriacetic acid (NTA) 40.0
Nitrobenzene 2.0
Paraquat 1.0
Parathion 5.0
PCBs 0.3
Pentachlorophenol 6.0
Phorate 0.2
Picloram 19.0
Pyridine 5.0
Selenium 1.0
Silver 5
Simazine 1.0
2,4,5-T (2,4,5-Trichlorophenoxyacetic acid) 28.0
2,4,5-TP/ Silvex/ 2-(2,4,5-Trichlorophenoxy)propionic acid 1.0
Temephos 28.0
Terbufos 0.1
Tetrachloroethylene 3.0
2,3,4,6-Tetrachlorophenol /(2,3,4,6-TeCP) 10.0
Toxaphene 0.5
Triallate 23.0
Trichloroethylene 5.0
2,4,5-Trichlorophenol (2,4,5-TCP) 400.0
2,4,6-Trichlorophenol (2,4,6-TCP) 0.5
Trifluralin 4.5
Uranium 10.0
Vinyl chloride 0.2

* Toxic equivalent (TEQ)

[O. Reg. 558/00, s. 5]

Schedule 5 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)

Slump

[O. Reg. 558/00, s. 5]

(c) Reproduced with permission from the Queen's Printer for Ontario