applies

applies is each individual hospital/medical/infectious waste incinerator (HMIWI) for which construction was commenced on or before June 20,1996. (2) A combustor is not subject to Rule 1.12 of these regulations during periods when only pathological waste, low-level radioactive waste, and/or chemotherapeutic waste is burned, provided the owner or operator of the combustor: (a) Notifies the Department of an exemption claim; and (b) Keeps records on a calendar quarter basis of the periods of time when only pathological waste, low-level radioactive waste, and/or chemotherapeutic waste is burned. (3) Any co-fired combustor is not subject to Rule 1.12 of these regulations if the owner or operator of the co-fired combustor: (a) Notifies the Department of an exemption claim; (b) Provides an estimate of the relative weight of hospital waste, medical/infectious waste, and other fuels and/or wastes to be combusted; and (c) Keeps records on a calendar quarter basis of the weight of hospital waste and medical/infectious waste combusted, and the weight of all other fuels and wastes combusted at the co-fired combustor. (4) Any combustor required to have a permit under Section 3005 of the Solid Waste Disposal Act is not subject to Rule 1.12 of these regulations. (5) Any combustor which meets the applicability requirements in standards or guidelines for certain municipal waste combustors under Subpart Cb, Ea, or Eb of 40 C.F.R. 60 is not subject to Section 12 of these regulations. (6) Any pyrolysis unit is not subject to Rule 1.12 of these regulations. (7) Cement kilns firing hospital waste and/or medical/infectious waste are not subject to Section 12 of these regulations. (8) Physical or operational changes made to an existing HMIWI unit solely for the purpose of complying with Rule 1.12 of these regulations are not considered a modification and do not result in an existing HMIWI unit becoming subject to the new source provisions under Rule 1.6 of these regulations and Subpart Ec of 40 C.F.R. 60. (9) Each existing HMIWI is subject to the permitting requirements in Title 11, Part 2, Chapter 6, Air Emissions Operating Permit Regulations for the Purposes of Title V of the Federal Clean Air Act,. Each owner and operator of an existing HMIWI shall submit an application for a Title V permit to the Department by December 15, 1999. (10) Beginning September 15, 2000, designated facilities subject to Rule 1.12 of these regulations shall operate pursuant to a permit issued under Title 11, Part 2, Chapter 6, Air Emissions Operating Permit Regulations for the Purposes of Title V of the Federal Clean Air Act. B. For the purpose of the requirements in Rule 1.12 of these regulations, the following definitions apply: (1) “Administrator of EPA” means the Administrator of the United States Environmental Protection Agency or his authorized representative. (2) “Batch HMIWI” means an HMIWI that is designed such that neither waste charging nor ash removal can occur during combustion. (3) “Biologicals” means preparations made from living organisms and their products, including vaccines, cultures, etc., intended for use in diagnosing, immunizing, or treating humans or animals or in research pertaining thereto. (4) “Blood products” means any product derived from human blood, including but not limited to blood plasma, platelets, red or white blood corpuscles, and other derived licensed products, such as interferon, etc. (5) “Body Fluids” means liquid emanating or derived from humans and limited to blood; dialysate; amniotic, cerebrospinal, synovial, pleural, peritoneal and pericardial fluids; and semen and vaginal secretions. (6) “Bypass stack” means a device used for discharging combustion gases to avoid severe damage to the air pollution control device or other equipment. (7) “Chemotherapeutic waste” means waste material resulting from the production or use of antineoplastic agents used for the purpose of stopping or reversing the growth of malignant cells. (8) “Co-fired combustor” means a unit combusting hospital waste and/or medical/infectious waste with other fuels or wastes (e.g., coal, municipal solid waste) and subject to an enforceable requirement limiting the unit to combusting a fuel feed stream, 10 percent or less of the weight of which is comprised, in aggregate, of hospital waste and medical/infectious waste as measured on a calendar quarter basis. For purposes of this definition, pathological waste, chemotherapeutic waste, and low- level radioactive waste are considered “other” wastes when calculating the percentage of hospital waste and medical/infectious waste combusted. (9) “Continuous emission monitoring system or CEMS” means a monitoring system for continuously measuring and recording the emissions of a pollutant from an affected facility. (10) “Continuous HMIWI” means an HMIWI that is designed to allow waste charging and ash removal during combustion. (11) “Dioxins/furans” means the combined emissions of tetra-through octa-chlorinated dibenzo-para-dioxins and dibenzofurans, as measured by EPA Reference Method 23. (12) “Dry scrubber” means an add-on air pollution control system that injects dry alkaline sorbent (dry injection) or sprays an alkaline sorbent (spray dryer) to react with and neutralize acid gases in the HMIWI exhaust stream forming a dry powder material. (13) “Fabric filter or baghouse” means an add-on air pollution control system that removes particulate matter (PM) and nonvaporous metals emissions by passing flue gas through filter bags. (14) “Facilities manager” means the individual in charge of purchasing, maintaining, and operating the HMIWI or the owner's or operator's representative responsible for the management of the HMIWI. Alternative titles may include Director of Facilities or Vice President of Support Services. (15) “High-air phase” means the stage of the batch operating cycle when the primary chamber reaches and maintains maximum operating temperatures. (16) “Hospital” means any facility which has an organized medical staff, maintains at least six inpatient beds, and where the primary function of the institution is to provide diagnostic and therapeutic patient services and continuous nursing care primarily to human inpatients who are not related and who stay on average in excess of 24 hours per admission. This definition does not include facilities maintained for the sole purpose of providing nursing or convalescent care to human patients who generally are not acutely ill but who require continuing medical supervision. (17) “Hospital/medical/infectious waste incinerator or HMIWI or HMIWI unit” means any device that combusts any amount of hospital waste and/or medical/infectious waste. (18) “Hospital/medical/infectious waste incinerator operator or HMIWI operator” means any person who operates, controls, or supervises the day-to-day operation of an HMIWI. (19) “Hospital waste” means discards generated at a hospital, except unused items returned to the manufacturer. The definition of hospital waste does not include human corpses, remains, and anatomical parts that are intended for interment or cremation. (20) “Infectious agent” means any organism (such as a virus or bacteria) that is capable of being communicated by invasion and multiplication in body tissues and capable of causing disease or adverse health impacts in humans. (21) “Intermittent HMIWI” means an HMIWI that is designed to allow waste charging, but not ash removal, during combustion. (22) “Large HMIWI” means: (a) Except as provided in subparagraph (b) (1) An HMIWI whose maximum design waste burning capacity is more than 500 pounds per hour; or (2) A continuous or intermittent HMIWI whose maximum charge rate is more than 500 pounds per hour; or (3) A batch HMIWI whose maximum charge rate is more than 4,000 pounds per day. (b) The following are not large HMIWI: (1) A continuous or intermittent HMIWI whose maximum charge rate is less than or equal to 500 pounds per hour; or (2) A batch HMIWI whose maximum charge rate is less than or equal to 4,000 pounds per day. (23) “Low-level radioactive waste” means waste material which contains radioactive nuclides emitting primarily beta or gamma radiation, or both, in concentrations or quantities that exceed applicable Federal or State standards for unrestricted release. Low-level radioactive waste is not high-level radioactive waste, spent nuclear fuel, or by-product material as defined by the Atomic Energy Act of 1954 [42 U.S.C. 2014 (e)(2)]. (24) “Malfunction” means any sudden, infrequent, and not reasonably preventable failure of air pollution control equipment, process equipment, or a process to operate in a normal or usual manner. Failures that are caused, in part, by poor maintenance or careless operation are not malfunctions. During periods of malfunction the operator shall operate within established parameters as much as possible, and monitoring of all applicable operating parameters shall continue until all waste has been combusted or until the malfunction ceases, whichever comes first. (25) “Maximum charge rate” means: (a) For continuous and intermittent HMIWI, 110 percent of the lowest 3-hour average charge rate measured during the most recent performance test demonstrating compliance with all applicable emission limits. (b) For batch HMIWI, 110 percent of the lowest daily charge rate measured during the most recent performance test demonstrating compliance with all applicable emission limits. (26) “Maximum design waste burning capacity” means: (a) For intermittent and continuous HMIWI, C= PV * 15,000 8,500 Where: C = HMIWI capacity, lb/hr PV = primary chamber volume, ft3 15,000 = primary chamber heat release rate factor, Btu/ft3/hr 8,500 = standard waste heating value, Btu/lb; (b) For batch HMIWI, C = PV * 4.5 Where: C = HMIWI capacity, lb/hr PV = primary chamber volume, ft3 4.5 = waste density, lb/ft; 8 = typical hours of operation of a batch HMIWI, hours. (27) “Maximum fabric filter inlet temperature” means 110 percent of the lowest 3-hour average temperature at the inlet to the fabric filter (taken, at a minimum, once every minute) measured during the most recent performance test demonstrating compliance with the dioxin/furan emission limit. (28) “Maximum flue gas temperature” means 110 percent of the lowest 3-hour average temperature at the outlet from the wet scrubber (taken, at a minimum, once every minute) measured during the most recent performance test demonstrating compliance with the mercury (Hg) emission limit. (29) “Medical/infectious waste” means any waste generated in the diagnosis, treatment, or immunization of human beings or animals, in research pertaining thereto, or in the production or testing of biologicals that is listed in paragraphs (a) through (g) of this definition. The definition of medical/infectious waste does not include ash from incineration of medical/infectious waste, once the incineration process has been completed; human corpses, remains, and anatomical parts that are intended for interment or cremation; and domestic sewage materials, hazardous waste, and household waste identified, listed, or defined in Part 261 of Mississippi Hazardous Waste Management Regulations. (a) Cultures and stocks of infectious agents and associated biologicals, including: cultures from medical and pathological laboratories; cultures and stocks of infectious agents from research and industrial laboratories; wastes from the production of biologicals; discarded live and attenuated vaccines; and culture dishes and devices used to transfer, inoculate, and mix cultures. (b) Human pathological waste, including tissues, organs, and body parts and body fluids that are removed during surgery or autopsy, or other medical procedures, and specimens of body fluids and their containers. (c) Human blood and blood products including: (1) Liquid waste human blood; (2) Products of blood; (3) Items saturated and/or dripping with human blood; or (4) Saturated and/or dripping with human blood that are now caked with dried human blood; including serum, plasma, and other blood components, and their containers, which were used or intended for use in either patient care, testing and laboratory analysis or the development of pharmaceuticals. Intravenous bags are also included in this category. (d) Sharps that have been used in animal or human patient care or treatment or in medical, research, or industrial laboratories, including hypodermic needles, syringes (with or without the attached needle), Pasteur pipettes, scalpel blades, blood vials, needles with attached tubing, and culture dishes (regardless of presence of infectious agents). Also included are other types of broken or unbroken glassware that were in contact with infectious agents, such as used slides and cover slips. (e) Animal waste including contaminated animal carcasses, body parts, and bedding of animals that were known to have been exposed to infectious agents during research (including research in veterinary hospitals), production of biologicals or testing of pharmaceuticals. (f) Isolation wastes including biological waste and discarded materials contaminated with blood, excretions, exudates, or secretions from humans who are isolated to protect others from certain highly communicable diseases, or isolated animals known to be infected with highly communicable diseases. (g) Unused sharps including the following unused, discarded sharps: hypodermic needles, suture needles, syringes, and scalpel blades. (30) “Medium HMIWI” means: (a) Except as provided in subparagraph (b) (1) An HMIWI whose maximum design waste burning capacity is more than 200 pounds per hour but less than or equal to 500 pounds per hour; or (2) A continuous or intermittent HMIWI whose maximum charge rate is more than 200 pounds per hour but less than or equal to 500 pounds per hour; or (3) A batch HMIWI whose maximum charge rate is more than 1,600 pounds per day but less than or equal to 4,000 pounds per day. (b) The following are not medium HMIWI: (1) A continuous or intermittent HMIWI whose maximum charge rate is less than or equal to 200 pounds per hour or more than 500 pounds per hour; or (2) A batch HMIWI whose maximum charge rate is more than 4,000 pounds per day or less than or equal to 1,600 pounds per day. (31) “Minimum dioxin/furan sorbent flow rate” means 90 percent of the highest 3-hour average dioxin/furan sorbent flow rate (taken, at a minimum, once every hour) measured during the most recent performance test demonstrating compliance with the dioxin/furan emission limit. (32) “Minimum Hg sorbent flow rate” means 90 percent of the highest 3-hour average Hg sorbent flow rate (taken, at a minimum, once every hour) measured during the most recent performance test demonstrating compliance with the Hg emission limit. (33) “Minimum hydrogen chloride (HCl) sorbent flow rate” means 90 percent of the highest 3-hour average HCl sorbent flow rate (taken, at a minimum, once every hour) measured during the most recent performance test demonstrating compliance with the HCl emission limit. (34) “Minimum horsepower or amperage” means 90 percent of the highest 3-hour average horsepower or amperage to the wet scrubber (taken, at a minimum, once every minute) measured during the most recent performance test demonstrating compliance with the applicable emission limits. (35) “Minimum pressure drop across the wet scrubber” means 90 percent of the highest 3- hour average pressure drop across the wet scrubber PM control device (taken, at a minimum, once every minute) measured during the most recent performance test demonstrating compliance with the PM emission limit. (36) “Minimum scrubber liquor flow rate” means 90 percent of the highest 3-hour average liquor flow rate at the inlet to the wet scrubber (taken, at a minimum, once every minute) measured during the most recent performance test demonstrating compliance with all applicable emission limits. (37) “Minimum scrubber liquor pH” means 90 percent of the highest 3-hour average liquor pH at the inlet to the wet scrubber (taken, at a minimum, once every minute) measured during the most recent performance test demonstrating compliance with the HC1 emission limit. (38) “Minimum secondary chamber temperature” means 90 percent of the highest 3-hour average secondary chamber temperature (taken, at a minimum, once every minute) measured during the most recent performance test demonstrating compliance with the PM, CO, or dioxin/furan emission limits. (39) “Modification or Modified HMIWI” means any change to an HMIWI unit after March 16, 1998, such that: (a) The cumulative costs of the modifications, over the life of the unit, exceed 50 per centum of the original cost of the construction and installation of the unit (not including the cost of any land purchased in connection with such construction or installation) updated to current costs, or (b) The change involves a physical change in or change in the method of operation of the unit which increases the amount of any air pollutant emitted by the unit for which standards have been established under Section 129 or Section 111 of the Federal Clean Air Act. (40) “Operating day” means a 24-hour period between 12:00 midnight and the following midnight during which any amount of hospital waste or medical/infectious waste is combusted at any time in the HMIWI. (41) “Operation” means the period during which waste is combusted in the incinerator excluding periods of startup or shutdown. (42) “Particulate matter or PM” means the total particulate matter emitted from an HMIWI as measured by EPA Reference Method 5 or EPA Reference Method 29. (43) “Pathological waste” means waste material consisting of only human or animal remains, anatomical parts, and/or tissue, the bags/containers used to collect and transport the waste material, and animal bedding (if applicable). (44) “Primary chamber” means the chamber in an HMIWI that receives waste material, in which the waste is ignited, and from which ash is removed. (45) “Pyrolysis” means the endothermic gasification of hospital waste and/or medical/infectious waste using external energy. (46) “Secondary chamber” means a component of the HMIWI that receives combustion gases from the primary chamber and in which the combustion process is completed. (47) “Shutdown” means the period of time after all waste has been combusted in the primary chamber. For continuous HMIWI, shutdown shall commence no less than 2 hours after the last charge to the incinerator. For intermittent HMIWI, shutdown shall commence no less than 4 hours after the last charge to the incinerator. For batch HMIWI, shutdown shall commence no less than 5 hours after the high-air phase of combustion has been completed. (48) “Small HMIWI” means: (a) Except as provided in subparagraph (b) (1) An HMIWI whose maximum design waste burning capacity is less than or equal to 200 pounds per hour; or (2) A continuous or intermittent HMIWI whose maximum charge rate is less than or equal to 200 pounds per hour; or (3) A batch HMIWI whose maximum charge rate is less than or equal to 1,600 pounds per day. (b) The following are not small HMIWI: (1) A continuous or intermittent HMIWI whose maximum charge rate is more than 200 pounds per hour. (2) A batch HMIWI whose maximum charge rate is more than 1,600 pounds per day. (49) “Standard conditions” means a temperature of 20DC and a pressure of 101.3 kilopascals. (50) “Standard Metropolitan Statistical Area or SMSA” means any areas listed in OMB Bulletin No. 93-17 entitled “Revised Statistical Definitions for Metropolitan Areas” dated June 30, 1993. (51) “Startup” means the period of time between the activation of the system and the first charge to the unit. For batch HMIWI, startup means the period of time between activation of the system and ignition of the waste. (52) “Wet scrubber” means an add-on air pollution control device that utilizes an alkaline scrubbing liquor to collect particulate matter (including nonvaporous metals and condensed organic) and/or to absorb and neutralize acid gases. C. Emission limits. (1) Except as provided for in subparagraph (2) no owner or operator of an affected facility shall cause to be discharged into the atmosphere from that affected facility any gases that contain stack emissions in excess of the limits presented in Table 1 of this paragraph. (2) The emission limits in Table 2 shall apply to any small HMIWI which is located more than 50 miles from the boundary of the nearest Standard Metropolitan Statistical Area (SMSA) and which burns less than 2,000 pounds per week of hospital waste and medical/infectious waste. The 2,000 lb/week limitation does not apply during performance tests. (3) No owner or operator of an affected facility shall cause to be discharged into the atmosphere from the stack of that affected facility any gases that exhibit greater than 10 percent opacity (6-minute block average). TABLE 1. EMISSION LIMITS FOR SMALL, MEDIUM, AND LARGE HMIWI Pollutant Units (7 percent oxygen, dry basis) Emission Limits HMIWI Size Small Medium Large Particulate matter Milligrams per dry standard cubic meter (grains per dry standard cubic foot) 115(0.05) 69 (0.03) 34(0.015) Carbon monoxide Parts per million by volume Dioxins/furans Nanograms per dry standard cubic meter total dioxins/furans (grains per billion dry standard cubic feet) or nanograms per dry standard cubic meter TEQ (grains per billion dry standard cubic feet) 125 (55) or 2.3(1.0) 125(55) or 2.3(1.0) 125(55) or 2.3(1.0) Hydrogen chloride Parts per million by volume or percent reduction 100 or 93% 100 or 93% 100 or 93% Sulfur dioxide Parts per million by volume Nitrogen oxides Parts per million by volume Lead Milligrams per dry standard cubic meter (grains per thousand dry standard cubic feet) or percent reduction 1.2(0.52) or 70% 1.2(0.52) or 70% 1.2(0.52) or 70% Cadmium Milligrams per dry standard cubic meter (grains per thousand dry standard cubic feet) or percent reduction 0.16(0.07) or 65% 0.16(0.07) or 65% 0.16(0.07) or 65% Mercury Milligrams per dry standard cubic meter (grains per thousand dry standard cubic feet) or percent reduction 0.55 (0.24) or 85% 0.55 (0.24) or 85% 0.55 (0.24) or 85% TABLE 2. EMISSION LIMITS FOR SMALL RURAL HMIWI Pollutant Units (7 percent oxygen, dry basis) HMIWI Emission Limits Particulate matter Milligrams per dry standard cubic meter (grains per dry standard cubic foot) 197(0.086) Carbon monoxide Parts per million by volume Dioxins/furans Nanograms per dry standard cubic meter total dioxins/furans (grains per billion dry standard cubic feet) or nanograms per dry standard cubic meter TEQ (grains per billion dry standard cubic feet) 800 (350) or 15(6.6) Hydrogen chloride Parts per million by volume Sulfur dioxide Parts per million by volume Nitrogen oxides Parts per million by volume Lead Milligrams per dry standard cubic meter (grains per thousand dry standard cubic feet) 10(4.4) Cadmium Milligrams per dry standard cubic meter (grains per thousand dry standard cubic feet) 4(1.7) Mercury Milligrams per dry standard cubic meter (grains per thousand dry standard cubic feet) 7.5 (3.3) D. Operator Training and Qualification Requirements. (1) Compliance with the requirements of this paragraph shall occur no later than September 15, 2000. (2) No owner or operator of an affected facility shall allow the affected facility to operate at any time unless a fully trained and qualified HMIWI operator is accessible, either at the facility or available within 1 hour. The trained and qualified HMIWI operator may operate the HMIWI directly or be the direct supervisor of one or more HMIWI operators. (3) Operator training and qualification shall be obtained through a State-approved program that meets the requirements included in subparagraphs (4) through (11) of this paragraph. (4) Training shall be obtained by completing an HMIWI operator training course that includes, at a minimum, the following provisions: (a) 24 hours of training on the following subjects: (1) Environmental concerns, including pathogen destruction and types of emissions; (2) Basic combustion principles, including products of combustion; (3) Operation of the type of incinerator to be used by the operator, including proper startup, waste charging, and shutdown procedures; (4) Combustion controls and monitoring; (5) Operation of air pollution control equipment and factors affecting performance (if applicable); (6) Methods to monitor pollutants (continuous emission monitoring systems and monitoring of HMIWI and air pollution control device operating parameters) and equipment calibration procedures (where applicable); (7) Inspection and maintenance of the HMIWI, air pollution control devices, and continuous emission monitoring systems; (8) Actions to correct malfunctions or conditions that may lead to malfunction; (9) Bottom and fly ash characteristics and handling procedures; (10) Applicable federal, state, and local regulations; (11) Work safety procedures; (12) Pre-startup inspections; and (13) Recordkeeping requirements. (b) An examination designed and administered by the instructor. (c) Reference material distributed to the attendees covering the course topics. (5) Qualification shall be obtained by: (a) Completion of a training course that satisfies the criteria under subparagraph (4) of this paragraph; and (b) Either 6 months experience as an HMIWI operator, 6 months experience as a direct supervisor of an HMIWI operator, or completion of at least two burn cycles under the observation of two qualified HMIWI operators. (6) Qualification is valid from the date on which the examination is passed or the completion of the required experience, whichever is later. (7) To maintain qualification, the trained and qualified HMIWI operator shall complete and pass an annual review or refresher course of at least 4 hours covering, at a minimum, the following: (a) Update of regulations; (b) Incinerator operation, including startup and shutdown procedures; (c) Inspection and maintenance; (d) Responses to malfunctions or conditions that may lead to malfunction; and (e) Discussion of operating problems encountered by attendees. (8) A lapsed qualification shall be renewed by one of the following methods: (a) For a lapse of less than 3 years, the HMIWI operator shall complete and pass a standard annual refresher course described in subparagraph (7) of this paragraph above. (b) For a lapse of 3 years or more, the HMIWI operator shall complete and pass a training course with the minimum criteria described in subparagraph (4) of this paragraph above. (9) The owner or operator of an affected facility shall maintain documentation at the facility that address the following: (a) Summary of the applicable standards under Rule 1.12 of these regulations; (b) Description of basic combustion theory applicable to an HMIWI; (c) Procedures for receiving, handling, and charging waste; (d) HMIWI startup, shutdown, and malfunction procedures; (e) Procedures for maintaining proper combustion air supply levels; (f) Procedures for operating the HMIWI and associated air pollution control systems within the standards established under Rule 1.12 of these regulations; (g) Procedures for responding to periodic malfunction or conditions that may lead to malfunction; (h) Procedures for monitoring HMIWI emissions; (i) Reporting and recordkeeping procedures; and (j) Procedures for handling ash. (10) The owner or operator of an affected facility shall establish a program for reviewing the information listed in subparagraph (9) of this paragraph annually with each HMIWI operator. (a) The initial review of the information listed in subparagraph (9) of this paragraph shall be conducted by March 15, 2000, or prior to assumption of responsibilities affecting HMIWI operation, whichever date is later. (b) Subsequent reviews of the information listed in subparagraph (9) of this paragraph shall be conducted annually. (11) The information listed in subparagraph (9) of this paragraph shall be kept in a readily accessible location for all HMIWI operators. This information, along with records of training shall be available for inspection by the Department upon request. E. Waste Management Guidelines. The owner or operator of an affected facility shall prepare a waste management plan. The waste management plan shall identify both the feasibility and the approach to separate certain components of solid waste from the health care waste stream in order to reduce the amount of toxic emissions from incinerated waste. A waste management plan may include, but is not limited to, elements such as paper, cardboard, plastics, glass, battery, or metal recycling; or purchasing recycled or recyclable products. A waste management plan may include different goals or approaches for different areas or departments of the facility and need not include new waste management goals for every waste stream. It should identify, where possible, reasonably available additional waste management measures, taking into account the effectiveness of waste management measures already in place, the costs of additional measures, the emission reductions expected to be achieved, and any other environmental or energy impacts they might have. The American Hospital Association publication entitled “An Ounce of Prevention: Waste Reduction Strategies for Health Care Facilities” shall be considered in the development of the waste management plan. F. Inspection Guidelines. (1) Requirements of this paragraph apply to any small HMIWI subject to the emission limits in Table 2 of paragraph C in Rule 1.12 of these regulations. (2) Later than September 15, 2000 and annually thereafter (no more than 12 months following the previous annual equipment inspection) an equipment inspection shall be performed. (a) At a minimum, an inspection shall include the following: (1) Inspect all burners, pilot assemblies, and pilot sensing devices for proper operation; clean pilot flame sensor, as necessary; (2) Ensure proper adjustment of primary and secondary chamber combustion air, and adjust as necessary; (3) Inspect hinges and door latches, and lubricate as necessary; (4) Inspect dampers, fans, and blowers for proper operation; (5) Inspect HMIWI door and door gaskets for proper sealing; (6) Inspect motors for proper operation; (7) Inspect primary chamber refractory lining; clean and repair/replace lining as necessary; (8) Inspect incinerator shell for corrosion and/or hot spots; (9) Inspect secondary/tertiary chamber and stack, clean as necessary; (10) Inspect mechanical loader, including limit switches, for proper operation, if applicable; (11) Visually inspect waste bed (grates), and repair/seal, as appropriate; (12) For the burn cycle that follows the inspection, document that the incinerator is operating properly and make any necessary adjustments; (13) Inspect air pollution control devices(s) for proper operation, if applicable; (14) Inspect waste heat boiler systems to ensure proper operation, if applicable; (15) Inspect bypass stack components; (16) Ensure proper calibration of thermocouples, sorbent feed systems, and any other monitoring equipment; and (17) Generally observe that the equipment is maintained in good operating condition. (b) Within 10 operating days following an equipment inspection, all necessary repairs shall be completed unless the owner or operator obtains written approval from the Department establishing a date whereby all necessary repairs of the designated facility shall be completed. G. Compliance and Performance Testing. (1) The emission limits under paragraph C in Rule 1.12 of these regulations shall apply at all times except during periods of startup, shutdown, or malfunction, provided that no hospital waste or medical/infectious waste is charged to the affected facility during startup, shutdown, or malfunction. (2) The owner or operator of an affected facility shall conduct an initial performance test in accordance with the performance test requirements contained in 40 C.F.R. 60.8 to determine compliance with the emission limits using the procedures and test methods listed in subparagraphs (2)(a) through (2)(j) of this paragraph. The use of the bypass stack during a performance test shall invalidate the performance test. (a) All performance tests shall consist of a minimum of three test runs conducted under representative operating conditions. (b) The minimum sample time shall be 1 hour per test run unless otherwise indicated. (c) EPA Reference Method 1 of Appendix A of 40 C.F.R. 60 shall be used to select the sampling location and number of traverse points. (d) EPA Reference Method 3 or 3 A of Appendix A of 40 C.F.R. 60 shall be used for gas composition analysis, including measurement of oxygen concentration. EPA Reference Method 3 or 3A of Appendix A of 40 C.F.R. 60 shall be used simultaneously with each reference method. (e) The pollutant concentrations shall be adjusted to 7 percent oxygen using the following equation: Where: Cadj = pollutant concentration adjusted to 7 percent oxygen; Cmeas = pollutant concentration measured on a dry basis; (20.9-7) = 20.9 percent oxygen - 7 percent oxygen (defined oxygen correction basis); 20.9 = oxygen concentration in air, percent; and %O2 = oxygen concentration measured on a dry basis, percent. (f) EPA Reference Method 5 or 29 Appendix A of 40 C.F.R. 60 shall be used to measure the particulate matter emissions. (g) EPA Reference method 9 of Appendix A of 40 C.F.R. 60 shall be used to measure stack opacity. (h) EPA Reference Method 10 or 10B of Appendix A of 40 C.F.R. 60 shall be used to measure the CO emissions. (i) EPA Reference Method 23 of Appendix A of 40 C.F.R. 60 shall be used to measure total dioxin/furan emissions. The minimum sample time shall be 4 hours per test run. If the affected facility has selected the toxic equivalency standards for dioxin/furans, under paragraph C in Rule 1.12 of these regulations, the following procedures shall be used to determine compliance: (1) Measure the concentration of each dioxin/furan tetra-through octa- congener emitted using EPA Reference Method 23. (2) For each dioxin/furan congener measured in accordance with subparagraph (2)(i)(1) of this paragraph, multiply the congener concentration by its corresponding toxic equivalency factor specified in Table 3 in Rule 1.12 of these regulations. (3) Sum the products calculated in accordance with subparagraph (2)(i)(2) of this paragraph to obtain the total concentration of dioxins/furans emitted in terms of toxic equivalency. ( ) ( ) C C O adj meas = − − . . % (j) EPA Reference Method 26 of Appendix A of 40 C.F.R. 60 shall be used to measure HCl emissions. If the affected facility has selected the percentage reduction standards for HCl under paragraph (C) in Rule 1.12 of these regulations, the percentage reduction in HCl emissions (%RHCI) is computed using the following formula: Where: (%RHCI) = percentage reduction of HCl emissions achieved; Ei = HCl emission concentration measured at the control device inlet, corrected to 7 percent oxygen (dry basis); and E0 = HCl emission concentration measured at the control device outlet, corrected to 7 percent oxygen (dry basis). (k) EPA Reference Method 29 of Appendix A of 40 C.F.R. 60 shall be used to measure Pb, Cd, and Hg emissions. If the affected facility has selected the percentage reduction standards for metals under paragraph (C) in Rule 1.12 of these regulations, the percentage reduction in emissions (%Rmetal) is computed using the following formula: Where: (%Rmetal) = percentage reduction of metal emission (Ph, Cd, or Hg) achieved; Ei = metal emission concentration (Pb, Cd, or Hg) measured at the control device inlet, corrected to 7 percent oxygen (dry basis); and E0 = metal emission concentration (Pb, Cd, or Hg) measured at the control device outlet, corrected to 7 percent oxygen (dry basis). ( ) %R E E E HCl i o i = −    100 ( ) %R E E E metal i o i = −      100 TABLE 3. TOXIC EQUIVALENCY FACTORS Dioxin/Furan Congener Toxic Equivalency Factor 2,3,7,8-tetrachlorinateddibenzo-p-dioxin 1,2,3,7,8-pentachlorinated dibenzo-p- dioxin 0.5 1,2,3,4,7,8- hexachlorinated dibenzo-p- dioxin 0.1 1,2,3,7,8,9-hexachlorinated dibenzo-p- dioxin 0.1 1,2,3,6,7,8-hexachlorinated dibenzo-p- dioxin 0.1 1,2,3,4,6,7,8-heptachlorinated dibenzo-p- dioxin 0.01 octachlorinated dibenzo-p-dioxin 0.001 2,3,7,8-tetrachlorinateddibenzofuran 0.1 2,3,4,7,8-pentachlorinateddibenzofuran 0.5 1,2,3,7,8-pentachlorinated dibenzofuran 0.05 1,2,3,4,7,8-hexachlorinated dibenzofuran 0.1 1,2,3,6,7,8-hexachlorinated dibenzofuran 0.1 1,2,3,7,8,9-hexachlorinated dibenzofuran 0.1 2,3,4,6,7,8-hexachlorinated dibenzofuran 0.1 1,2,3,4,6,7,8-heptachlorinated dibenzofuran 0.01 1,2,3,4,7,8,9-heptachIorinated dibenzofuran 0.01 octachlorinated dibenzofuran 0.001 (3) Following the date on which the initial performance test is completed or is required to be completed under the performance test requirements contained in 40 C.F.R. 60.8, whichever date comes first, the owner or operator of an affected facility shall: (a) Determine compliance with the opacity limit by conducting an annual performance test (no more than 12 months following the previous performance test) using the applicable procedures and test methods listed in subparagraph (2) of this paragraph. (b) Determine compliance with the PM, CO, and HCl emission limits by conducting an annual performance test (no more than 12 months following the previous performance test) using the applicable procedures and test methods listed in subparagraph (2) of this paragraph. If all three performance tests over a 3-year period indicate compliance with the emission limit for a pollutant (PM, CO, or HCl), the owner or operator may forego a performance test for that pollutant for the subsequent 2 years. At a minimum, a performance test for PM, CO, and HCl shall be conducted every third year (no more than 36 months following the previous performance test). If a performance test conducted every third year indicates compliance with the emission limit for a pollutant (PM, CO, or HCl), the owner or operator may forego a performance test for that pollutant for up to an additional 2 years. If any performance test indicates noncompliance with the respective emission limit, a performance test for that pollutant shall be conducted annually until all annual performance tests over a 3-year period indicate compliance with the emission limit. The use of the bypass stack during a performance test shall invalidate the performance test. (c) Facilities using a CEMS to demonstrate compliance with any of the emission limits under paragraph C in Rule 1.12 of these regulations shall: (1) Determine compliance with the appropriate emission limit(s) using a 12-hour rolling average, calculated each hour as the average of the previous 12 operating hours (not including startup, shutdown, or malfunction). (2) Operate all CEMS in accordance with the applicable procedures under Appendices B and F of 40 C.F.R. 60. (4) The owner or operator of an affected facility equipped with a dry scrubber followed by a fabric filter, a wet scrubber, or a dry scrubber followed by a fabric filter and wet scrubber shall: (a) Establish the appropriate maximum and minimum operating parameters, indicated in Table 4 of Rule 1.12 of these regulations for each control system, as site specific operating parameters during the initial performance test to determine compliance with the emission limits; and (b) Following the date on which the initial performance test is completed or is required to be completed under the performance test requirements contained in 40 C.F.R. 60.8, whichever date comes first, ensure that the affected facility does not operate above any of the applicable maximum operating parameters or below any of the applicable minimum operating parameters listed in Table 4 in Rule 1.12 of these regulations and measured as 3-hour rolling averages (calculated each hour as the average of the previous 3 operating hours) at all times except during periods of startup, shutdown, and malfunction. Operating parameter limits do not apply during performance tests. Operation above the established maximum or below the established minimum operating parameter(s) shall constitute a violation of established operating parameter(s). (5) Except as provided in subparagraph (8) of this paragraph, for affected facilities equipped with a dry scrubber followed by a fabric filter: (a) Operation of the affected facility above the maximum charge rate and below the minimum secondary chamber temperature (each measured on a 3-hour rolling average) simultaneously shall constitute a violation of the CO emission limit. (b) Operation of the affected facility above the maximum fabric filter inlet temperature, above the maximum charge rate, and below the minimum dioxin/furan sorbent flow rate (each measured on a 3-hour rolling average) simultaneously shall constitute a violation of the dioxin/furan emission limit. (c) Operation of the affected facility above the maximum charge rate and below the minimum HCl sorbent flow rate (each measured on a 3-hour rolling average) simultaneously shall constitute a violation of the HCl emission limit. (d) Operation of the affected facility above the maximum charge rate and below the minimum Hg sorbent flow rate (each measured on a 3-hour rolling average) simultaneously shall constitute a violation of the Hg emission limit. (e) Use of the bypass stack (except during startup, shutdown, or malfunction) shall constitute a violation of the PM, dioxin/furan, HCl, Pb, Cd and Hg emission limits. (6) Except as provided in subparagraph (8) of this paragraph, for affected facilities equipped with a wet scrubber: (a) Operation of the affected facility above the maximum charge rate and below the minimum pressure drop across the wet scrubber or below the minimum horsepower or amperage to the system (each measured on a 3- hour rolling average) simultaneously shall constitute a violation of the PM emission limit. (b) Operation of the affected facility above the maximum charge rate and below the minimum secondary chamber temperature (each measured on a 3-hour rolling average) simultaneously shall constitute a violation of the CO emission limit. (c) Operation of the affected facility above the maximum charge rate, below the minimum secondary chamber temperature, and below the minimum scrubber liquor flow rate (each measured on a 3-hour rolling average) simultaneously shall constitute a violation of the dioxin/furan emission limit. (d) Operation of the affected facility above the maximum charge rate and below the minimum scrubber liquor pH (each measured on a 3-hour rolling average) simultaneously shall constitute a violation of the HCl emission limit. (e) Operation of the affected facility above the maximum flue gas temperature and above the maximum charge rate (each measured on a 3-hour rolling average) simultaneously shall constitute a violation of the Hg emission limit. (f) Use of the bypass stack (except during startup, shutdown, or malfunction) shall constitute a violation of the PM, dioxin/furan, HCl, Pb, Cd and Hg emission limits. (7) Except as provided in subparagraph (h) of this paragraph, for affected facilities equipped with a dry scrubber followed by a fabric filter and a wet scrubber: (a) Operation of the affected facility above the maximum charge rate and below the minimum secondary chamber temperature (each measured on a 3-hour rolling average) simultaneously shall constitute a violation of the CO emission limit. (b) Operation of the affected facility above the maximum fabric filter inlet temperature, above the maximum charge rate, and below the minimum dioxin/furan sorbent flow rate (each measured on a 3-hour rolling average) simultaneously shall constitute a violation of the dioxin/furan emission limit. (c) Operation of the affected facility above the maximum charge rate and below the minimum scrubber liquor pH (each measured on a 3-hour rolling average) simultaneously shall constitute a violation of the HCl emission limit. (d) Operation of the affected facility above the maximum charge rate and below the minimum Hg sorbent flow rate (each measured on a 3-hour rolling average) simultaneously shall constitute a violation of the Hg emission limit. (e) Use of the bypass stack (except during startup, shutdown, or malfunction) shall constitute a violation of the PM, dioxin/furan, HCl, Pb, Cd and Hg emission limits. (8) The owner or operator of an affected facility may conduct a repeat performance test within 30 days of violation of applicable operating parameter(s) to demonstrate that the affected facility is not in violation of the applicable emission limit(s). Repeat performance tests conducted pursuant to this paragraph shall be conducted using the identical operating parameters that indicated a violation under subparagraph (5), (6), or (7) of this paragraph. (9) The owner or operator of an affected facility using an air pollution control device other than a dry scrubber followed by a fabric filter, a wet scrubber, or a dry scrubber followed by a fabric filter and a wet scrubber to comply with the emission limits under paragraph C in Rule 1.12 of these regulations shall petition the Administrator for other site-specific operating parameters to be established during the initial performance test and continuously monitored thereafter. The owner or operator shall not conduct the initial performance test until after the petition has been approved by the Administrator. (10) The owner or operator of an affected facility may conduct a repeat performance test at any time to establish new values for the operating parameters. The Department may request a repeat performance test at any time. (11) Any small HMIWI subject to the emission limits in Table 2 of paragraph C in