ALABAMA DEPARTMENT OF ENVIRONMENTAL MANAGEMENT

AIR DIVISION

ADMINISTRATIVE CODE

CHAPTER 335-3-19 CONTROL OF MUNICIPAL SOLID WASTE LANDFILL GAS EMISSIONS

TABLE OF CONTENTS

335-3-19-.01 Definitions

335-3-19-.02 General Provisions

335-3-19-.03 Standards For Existing Municipal Solid Waste Landfills

335-3-19-.04 Compliance Schedules

335-3-19-.05 Petition For Alternative Standards And Compliance Schedules

335-3-19-.01 Definitions. For the purposes of this Chapter and Rule 335-3-10-.02(75) only, the following words and phrases, unless a different meaning is plainly required by the content, shall have the following meanings.

(a) "Active collection system" means a gas collection system that uses gas mover equipment.

(b) "Active landfill" means a landfill in which solid waste is being placed or a landfill that is planned to accept waste in the future.

(c) "Closed landfill" means a landfill in which solid waste is no longer being placed, and in which no additional solid wastes will be placed without first filing a notification of modification as prescribed under §60.7(a)(4), 40 CFR. Once a notification of modification has been filed, and additional solid waste is placed in the landfill, the landfill is no longer closed.

(d) "Closure" means that point in time when a landfill becomes a closed landfill.

(e) "Commercial solid waste" means all types of solid waste generated by stores, offices, restaurants, warehouses, and other nonmanufacturing activities, excluding residential and industrial wastes.

(f) "Controlled landfill" means any landfill at which collection and control systems are required under this Chapter as a result of the nonmethane organic compounds emission rate. The landfill is considered controlled at the time a collection and control system design plan is submitted in compliance with Rule 335-3-19-.03(1)(b)2.(i).

(g) "Design capacity" means the maximum amount of solid waste a landfill can accept, as indicated in terms of volume or mass in the most recent permit issued by the Department, plus any in-place waste not accounted for in the most recent permit. If the owner or operator chooses to convert the design capacity from volume to mass or from mass to volume to demonstrate its design capacity is less than 2.5 million megagrams or 2.5 million cubic meter, the calculation must include a site specific density, which must be recalculated annually.

(h) "Emission rate cutoff" means the threshold annual emission rate to which a landfill compares its estimated emission rate to determine if control under the regulation is required.

(i) "Enclosed combustor" means an enclosed firebox which maintains a relatively constant limited peak temperature generally using a limited supply of combustion air. An enclosed flare is considered an enclosed combustor.

(j) "Flare" means an open combustor without enclosure or shroud.

(k) "Gas mover equipment" means the equipment (i.e., fan, blower, compressor) used to transport landfill gas through the header system.

(l) "Household waste" means any solid waste including garbage and trash derived from households (including, but not limited to, single and multiple residences, hotels and motels, bunkhouses, ranger stations, crew quarters, campgrounds, picnic grounds, and day-use recreation areas).

(m) "Industrial solid waste" means solid waste generated by manufacturing or industrial processes that is not a hazardous waste regulated under Subtitle C of the Resource Conservation and Recovery Act. Such waste may include, but is not limited to, waste resulting from the following manufacturing processes: electric power generation; fertilizer/agricultural chemicals; food and related products/by-products; inorganic chemicals; iron and steel manufacturing; leather and leather products; nonferrous metals manufacturing/foundries; organic chemicals; plastics and resins manufacturing; pulp and paper industry; rubber and miscellaneous plastic products; stone, glass, clay, and concrete products; textile manufacturing; transportation equipment; and water treatment. This term does not include fly ash waste, bottom ash waste, boiler slag waste, or flue gas emission control waste which result from the combustion of coal or other fossil fuels at electric or steam generating plants. Additionally, this term does not include mining waste or oil and gas wastes, or small quantity generator waste as defined in ADEM Admin. Code R. 335-14-2-.01(5). Uncontaminated concrete, soil, brick, rock, and similar materials are excluded from this definition.

(n) "Interior Well" means any well or similar collection component located inside the perimeter of the landfill waste. A perimeter well located outside the landfilled waste is not an interior well.

(o) "Landfill" means an area of land or an excavation in which wastes are placed for permanent disposal, and that is not a land application unit, surface impoundment, injection well, or waste pile as those terms are defined under ADEM Admin. Code R. 335-13-1-.03.

(p) "Lateral expansion" means a horizontal expansion of the waste boundaries of an existing MSW landfill. A lateral expansion is not a modification unless it results in an increase in the design capacity of the landfill.

(q) "Modification" means an increase in the permitted volume design capacity of the landfill by either horizontal or vertical expansion based on its design capacity as of May 30, 1991. Modification does not occur until the owner or operator commence construction on the horizontal or vertical expansion.

(r) "Municipal solid waste landfill" or "MSW landfill" means an entire disposal facility in a contiguous geographic space where household waste is placed in or on land.  An MSW landfill may also receive other types of RCRA Subtitle D wastes (ADEM Admin. Code R. 335-13-1-.03) such as commercial solid waste, nonhazardous sludge, conditionally exempt small quantity generator waste, and industrial solid waste.  Portions of an MSW landfill may be separated by access roads.  An MSW landfill may be publicly or privately owned.  An MSW landfill may be a new MSW landfill, an existing MSW landfill, or a lateral expansion.

(s) "Municipal solid waste landfill emissions" or "MSW landfill emissions" means gas generated by the decomposition of organic waste deposited in an MSW landfill or derived from the evolution of organic compounds in the waste.

(t) "NMOC" means nonmethane organic compounds, as measured according to the provisions of Rule 335-3-19-.03(3).

(u) "Nondegradable waste" means any waste that does not decompose through chemical breakdown or microbiological activity.  Examples are, but are not limited to, concrete, municipal waste combustor ash, and metals.

(v) "Passive collection system" means a gas collection system that solely uses positive pressure within the landfill to move the gas rather than using gas mover equipment.

(w) "Sludge" means any nonhazardous solid, semisolid, or liquid waste generated from a municipal, commercial, or industrial wastewater treatment plant, water supply treatment plant, or air pollution control facility, exclusive of the treated effluent from a wastewater treatment plant.

(x) "Solid waste" means any garbage or rubbish, construction/demolition debris, ash, sludge from a wastewater treatment plant, water supply treatment plant, or air pollution control facility and other discarded material, including solid, liquid, semisolid, or contained gaseous material resulting from industrial, commercial, mining, and agricultural operations, and from community activities or materials intended for or capable of recycling, but which have not been diverted or removed from the solid waste stream. The term "solid waste" does not include recovered material, solid or dissolved material in domestic sewage, or solid or dissolved materials in irrigation return flows or industrial discharges that are point sources subject to National Pollutant Discharge permits under the Federal Water Pollution Control Act 33 U.S.C. 1342, as amended, or source, special nuclear, or by-product material as defined by the Atomic Energy Act of 1954, as amended (42 U.S.C. 2011 et seq.). Also excluded from this definition are wastes from silvicultural operations, land application of crop residues, animal residues, animal manure and ash resulting exclusively from the combustion of fossil fuels or wood during normal agricultural operations or mining refuse as defined and regulated pursuant to the Alabama Mining Act.

(y) "Sufficient density" means any number, spacing, and combination of collection system components, including vertical wells, horizontal collectors, and surface collectors, necessary to maintain emission and migration control as determined by measures of performance set forth in this Chapter.

(z) "Sufficient extraction rate" means a rate sufficient to maintain a negative pressure at all wellheads in the collection system without causing air infiltration, including any wellheads connected to the system as a result of expansion or excess surface emissions, for the life of the blower.

Author: Ronald W. Gore

Statutory Authority: Code of Ala. 1975, §§22-28-14, 22-22A-5, 22-22A-6, 22-22A-8.

History: New Rule: Filed December 11, 1997; effective January 15, 1998. Amended: Filed December 9, 1999; effective January 13, 2000.

335-3-19-.02 General Provisions.

(1) The provisions of this Chapter apply to each existing MSW landfill for which construction, reconstruction or modification was commenced before May 30, 1991. Physical or operational changes made to an existing MSW landfill solely to comply with this Chapter are not considered a modification or reconstruction and would not subject an existing MSW landfill to the requirements of Subpart WWW as incorporated by reference in Rule 335-3-10-.02(75), [see §60.750 of Subpart WWW, 40 CFR].

(2) Control of MSW landfill emissions shall be required at each MSW landfill meeting the following three conditions:

(a) The landfill has accepted municipal solid waste at any time since November 8, 1987;

(b) The landfill has a design capacity greater than or equal to 2.5 million megagrams and 2.5 million cubic meters.  The landfill may calculate design capacity in either megagrams or cubic meters for comparison with the exemption values.  Any density conversions shall be documented and submitted with the design capacity report; and

(c) The landfill has a nonmethane organic compound emission rate of 50 megagrams per year or more.

(3) For purposes of obtaining an operating permit under Chapter 335-3-16 of this Division, the owner or operator of a MSW landfill subject to this Chapter with a design capacity less than 2.5 million megagrams or 2.5 million cubic meters is not subject to the requirements to obtain an operating permit for the landfill under Chapter 335-3-16, unless the landfill is otherwise subject to Chapter 335-3-16. For purposes of submitting a timely application for an operating permit, the owner or operator of a MSW landfill subject to this Chapter with a design capacity greater than or equal to 2.5 million megagrams and 2.5 million cubic meters on the effective date of EPA’s approval of the state’s program [December 7, 1998], and not otherwise subject to Chapter 335-3-16, becomes subject to the requirements of Chapter 335-3-16, 90 days after the effective date [March 7, 1999] of said program approval, even if the design capacity report is submitted earlier.

(4) When a MSW landfill subject to this Chapter is closed, the owner or operator is no longer subject to the requirement to maintain an operating permit under Chapter 335-3-16 for the landfill if the landfill is not otherwise subject to the requirements of Chapter 335-3-16 and if either of the following conditions are met.

(a) The landfill was never subject to the requirement for a control system under Rule 335-3-19-.03; or

(b) The owner or operator meets the condition for control system removal specified in Rule 335-3-19-.03(1)(b)2.(v).

Author: Ronald W. Gore

Statutory Authority: Code of Ala. 1975, §§22-28-14, 22-22A-5, 22-22A-6, 22-22A-8.

History: New Rule: Filed December 11, 1997; effective January 15, 1998. Amended: Filed December 9, 1999; effective January 13, 2000.

335-3-19-.03 Standards For Existing Municipal Solid Waste Landfills.

(1) Standards for Air Emissions from Existing Municipal Solid Waste Landfills.

(a) Each owner or operator of an MSW landfill having a design capacity less than 2.5 million megagrams by mass or 2.5 million cubic meters by volume shall submit an initial design capacity report to the Director as provided in subparagraph(6)(a) of this Rule.  The landfill may calculate design capacity in either megagrams or cubic meters for comparison with the exemption values.  Any density conversions shall be documented and submitted with the report. Submittal of the initial design capacity report shall fulfill the requirements of this Rule except as provided for in subparagraphs (a)1. and (a)2. below.

1. The owner or operator shall submit to the Director an amended design capacity report, as provided for in subparagraph(6)(a)3. [Guidance: Note that if the design capacity increase is the result of a modification, as defined in Rule 335-3-19-.01, that was commenced construction on or after May 30, 1991, the landfill will become subject to Rule 335-3-10-.02(75), 40 CFR 60, Subpart WWW. If the design capacity increase is the result of a change in operating practices, density, or some other change that is not a modification, the landfill remains subject to this Chapter.]

2. When an increase in the maximum design capacity of a landfill with an initial design capacity less than 2.5 million megagrams or 2.5 million cubic meters results in a revised maximum design capacity equal to or greater than 2.5 million megagrams and 2.5 million cubic meters, the owner or operator shall comply with the provision of subparagraph (b) below.

(b) Each owner or operator of an MSW landfill having a design capacity equal to or greater than 2.5 million megagrams and 2.5 million cubic meters, shall either comply with subparagraph (b)2. of this paragraph or calculate an NMOC emission rate for the landfill using the procedures specified in paragraph (3) of this Rule. The NMOC emission rate shall be recalculated annually, except as provided in subparagraph (6)(b)1.(ii) of this Rule. The owner or operator of an MSW landfill subject to this Chapter with a design capacity greater than or equal to 2.5 million megagrams and 2.5 million cubic meters is subject to major source operating permitting requirements in Chapter 335-3-16.

1. If the calculated NMOC emission rate is less than 50 megagrams per year, the owner or operator shall:

(i) submit an annual emission report to the Director, except as provided for in subparagraph(6)(b)1.(ii) of this Rule; and

(ii) recalculate the NMOC emission rate annually using the procedures specified in subparagraph (3)(a) of this Rule until such time as the calculated NMOC emission rate is equal to or greater than 50 megagrams per year, or the landfill is closed.

(I) If the NMOC emission rate, upon initial calculation or annual recalculation required in subparagraph (b)1.(ii) above, is equal to or greater than 50 megagrams per year, the owner or operator shall install a collection and control system in compliance with subparagraph (b)2. below.

(II) If the landfill is permanently closed, a closure notification shall be submitted to the Director as provided for in subparagraph (6)(d) of this Rule.

2. If the calculated NMOC emission rate is equal to or greater than 50 megagrams per year, the owner or operator shall:

(i) Submit a collection and control system design plan prepared by a professional engineer to the Director within 1 year:

(I) The collection and control system as described in the plan shall meet the design requirements of subparagraph (b)2.(ii) of this paragraph, below.

(II) The collection and control system design plan shall include any alternatives to the operational standards, test methods, procedures, compliance measures, monitoring, recordkeeping or reporting provisions of paragraphs (2) through (7) of this Rule proposed by the owner or operator.

(III) The collection and control system design plan shall either conform with specifications for active collection systems in paragraph (8) of this Rule or include a demonstration to the Director’s satisfaction of the sufficiency of the alternative provisions to paragraph (8) of this Rule.

(IV) The Director shall review the information submitted under subparagraphs (b)2.(i)(I), (II) and (III) of this paragraph and either approve it, disapprove it, or request that additional information be submitted. Because of the many site-specific factors involved with landfill gas system design, alternative systems may be necessary. A wide variety of system designs are possible, such as vertical wells, combination horizontal and vertical collection systems, or horizontal trenches only, leachate collection components, and passive systems.

(ii) Install a collection and control system that captures the gas generated within the landfill as required by Rule 335-3-19-.03(1)(b)2.(ii)(I) or (II) and (b)2.(iii) of this Chapter within 30 months after the first annual report in which the emission rate equals or exceeds 50 megagrams per year, unless Tier 2 or Tier 3 sampling demonstrates that the emission rate is less than 50 megagrams per year, as specified in subparagraph (6)(c)1. or 2. of this Rule.

(I) An active collection system shall:

I. Be designed to handle the maximum expected gas flow rate from the entire area of the landfill that warrants control over the intended use period of the gas control or treatment system equipment;

II. Collect gas from each area, cell, or group of cells in the landfill in which the initial solid waste has been placed for a period of:

A. 5 years or more if active; or

B. 2 years or more if closed or at final grade;

III. Collect gas at a sufficient extraction rate;

IV. Be designed to minimize off-site migration of subsurface gas.

(II) A passive collection system shall:

I. Comply with the provisions specified in subparagraphs (I)I., (I)II., and (I)IV. of subparagraph (b)2.(ii) of this paragraph.

II. Be installed with liners on the bottom and all sides in all areas in which gas is to be collected. The liners shall be installed as required under ADEM Admin. Code Chapter 335-13-4.

(iii) Route all the collected gas to a control system that complies with the requirements in either subparagraph (b)2.(iii)(I), (II) or (III) below.

(I) An open flare designed and operated in accordance with §60.18, 40 CFR;

(II) A control system designed and operated to reduce NMOC by 98 weight-percent, or, when an enclosed combustion device is used for control, to either reduce NMOC by 98 weight percent or reduce the outlet NMOC concentration to less than 20 parts per million by volume, dry basis as hexane at 3 percent oxygen. The reduction efficiency or parts per million by volume shall be established by an initial performance test to be completed no later than 180 days after initial startup of the approved control system, using the test methods specified in subparagraph(3)(d) of this Rule.

I. If a boiler or process heater is used as the control device, the landfill gas stream shall be introduced into the flame zone.

II. The control device shall be operated within the parameter ranges established during the initial or most recent performance test. The operating parameters to be monitored are specified in paragraph (5) of this Rule;

(III) Route the collected gas to a treatment system that processes the collected gas for subsequent sale or use. All emissions from any atmospheric vent from the gas treatment system shall be subject to the requirements of subparagraph (b)2.(iii)(I) or (II) of this paragraph.

(iv) Operate the collection and control device installed to comply with this Chapter in accordance with the provisions of paragraphs (2), (4) and (5) of this Rule.

(v) The collection and control system may be capped or removed provided that all the conditions of subparagraphs (b)2.(v)(I), (II), and (III) of this paragraph below are met:

(I) The landfill shall be a closed landfill as defined in Rule 335-3-19-.01(c). A closure report shall be submitted to the Director as provided in subparagraph (6)(d) of this Rule;

(II) The collection and control system shall have been in operation a minimum of 15 years; and

(III) Following the procedures specified in subparagraph (3)(b) of this Rule, the calculated NMOC gas produced by the landfill shall be less than 50 megagrams per year on three successive test dates. The test dates shall be no less than 90 days apart, and no more than 180 days apart.

(2) Operational Standards for Collection and Control Systems. Each owner or operator of an MSW landfill with a gas collection and control system used to comply with the provisions of subparagraph (1)(b)2.(ii) of this Rule shall:

(a) Operate the collection system such that gas is collected from each area, cell, or group of cells in the MSW landfill in which solid waste has been in place for:

1. 5 years or more if active; or

2. 2 years or more if closed or at final grade;

(b) Operate the collection system with negative pressure at each wellhead except under the following conditions:

1. a fire or increased well temperature. The owner or operator shall record instances when positive pressure occurs in efforts to avoid a fire. These records shall be submitted with the annual reports as provided in subparagraph (6)(f)1. of this Rule;

2. use of a geomembrane or synthetic cover. The owner or operator shall develop acceptable pressure limits in the design plan;

3. a decommissioned well. A well may experience a static positive pressure after shut down to accommodate for declining flows. All design changes shall be approved by the Director;

(c) Operate each interior wellhead in the collection system with a landfill gas temperature less than 55oC and with either a nitrogen level less than 20 percent or an oxygen level less than 5 percent. The owner or operator may establish a higher operating temperature, nitrogen, or oxygen value at a particular well. A higher operating value demonstration shall show supporting data that the elevated parameter does not cause fires or significantly inhibit anaerobic decomposition by killing methanogens.

1. the nitrogen level shall be determined using Method 3C (40 CFR 60), unless an alternative test method is established as allowed by subparagraph (1)(b)2.(i) of this Rule.

2. unless an alternative test method is established as allowed by subparagraph (1)(b)2.(i) of this Rule, the oxygen shall be determined by an oxygen meter using Method 3A (40 CFR 60) except that:

(i) the span shall be set so that the regulatory limit is between 20 and 50 percent of the span;

(ii) a data recorder is not required;

(iii) only two calibration gases are required, a zero and span, and ambient air may be used as the span;

(iv) a calibration error check is not required;

(v) the allowable sample bias, zero drift, and calibration drift are ± 10 percent.

(d) Operate the collection system so that the methane concentration is less than 500 parts per million above background at the surface of the landfill. To determine if this level is exceeded, the owner or operator shall conduct surface testing around the perimeter of the collection area and along a pattern that traverses the landfill at 30 meter intervals and where visual observations indicate elevated concentrations of landfill gas, such as distressed vegetation and cracks or seeps in the cover. The owner or operator may establish an alternative traversing pattern that ensures equivalent coverage. A surface monitoring design plan shall be developed that includes a topographical map with the monitoring route and the rationale for any site-specific deviations from the 30 meter intervals. Areas with steep slopes or other dangerous areas may be excluded from the surface testing.

(e) Operate the system such that all collected gases are vented to a control system designed and operated in compliance with subparagraph (1)(b)2.(iii) of this Rule. In the event the collection or control system is inoperable, the gas mover system shall be shut down and all valves in the collection and control system contributing to venting of the gas to the atmosphere shall be closed within 1 hour; and

(f) Operate the control or treatment system at all times when the collected gas is routed to the system.

(g) If monitoring demonstrates that the operational requirement in subparagraphs (b), (c), or (d) of this paragraph are not met, corrective action shall be taken as specified in subparagraphs (4)(a)3. through 5. or subparagraph (4)(c) of this Rule. If corrective actions are taken as specified in paragraph (4) of this Rule, the monitored exceedance is not a violation of the operational requirements in this paragraph.

(3) Test Methods and Procedures.

(a) The landfill owner or operator shall calculate the NMOC emission rate using either the equation provided in subparagraph (a)1. of this paragraph or the equation provided in subparagraph (a)1.(ii) of this paragraph. Both equations may be used if the actual year-to-year solid waste acceptance rate is known, as specified in subparagraph (a)1. of this paragraph, for part of the life of the landfill and the actual year-to-year solid waste acceptance rate if unknown, as specified in subparagraph (a)1.(ii) of this paragraph, for part of the life of the landfill. The values to be used in both equations are 0.05 per year for k, 170 cubic meters per megagram for Lo, and 4,000 parts per million by volume as hexane for the CNMOC.

1. The following equation shall be used if the actual year-to-year solid waste acceptance rate is known.

where,

MNMOC 

= 

Total NMOC emission rate from the landfill, megagrams per year 

k 

= 

methane generation rate constant, year-1 

Lo 

= 

methane generation potential, cubic meters per megagram solid waste 

Mi 

= 

mass of solid waste in the ith section, megagrams 

ti 

= 

age of the ith section, years 

CNMOC 

= 

concentration of NMOC, parts per million by volume as hexane 

3.6 x 10-9 

= 

conversion factor 

(i) The mass of nondegradable solid waste may be subtracted from the total mass of solid waste in a particular section of the landfill when calculating the value for Mi if the documentation of the nature and amount of such wastes is maintained.

(ii) The following equation shall be used if the actual year-to-year solid waste acceptance rate is unknown.

where,

MNMOC 

= 

mass emission rate of NMOC, megagrams per year 

Lo 

= 

methane generation potential, cubic meters per megagram solid waste 

R 

= 

average annual acceptance rate, megagrams per year 

k 

= 

methane generation rate constant, year-1 

t 

= 

age of landfill, years 

CNMOC 

= 

concentration of NMOC, parts per million by volume as hexane 

c 

= 

time since closure, years.  For active landfill c = 0 and e-kc = 1 

3.6 x 10-9 

= 

conversion factor 

(iii) The mass of nondegradable solid waste may be subtracted from the total mass of solid waste in a particular section of the landfill when calculating a value for R, if the documentation of the nature and amount of such wastes is maintained.

2. Tier 1. The owner or operator shall compare the calculated NMOC mass emission rate to the standard of 50 megagrams per year.

(i) If the NMOC emission rate calculated in subparagraph (a)1. of this paragraph is less than 50 megagrams per year, then the landfill owner shall submit an emission rate report as provided in subparagraph (6)(b)1. of this Rule, and shall recalculate the NMOC mass emission rate annually as required under subparagraph (1)(b)1. of this Rule.

(ii) If the calculated NMOC emission rate is equal to or greater than 50 megagrams per year, then the landfill owner shall either comply with subparagraph (1)(b)2. of this Rule, or determine a site-specific NMOC concentration and recalculate the NMOC emission rate using the procedures provided in subparagraph (a)3. of this paragraph.

3. Tier 2. The landfill owner or operator shall determine the NMOC concentration using the following sampling procedure. The landfill owner or operator shall install at least two sample probes per hectare of landfill surface that has retained waste for at least 2 years. If the landfill is larger than 25 hectares in area, only 50 samples are required. The sample probes should be located to avoid known areas of nondegradable solid waste. The owner or operator shall collect and analyze one sample of landfill gas from each probe to determine the NMOC concentration using Method 25C of Appendix A or Method 18 of Appendix A (40 CFR 60). If using Method 18 of Appendix A, the minimum list of compounds to be tested shall be those published in the most recent Compilation of Air Pollutant Emission Factors (AP-42). If composite sampling is used, equal volumes shall be taken from each sample probe.  If more than the required number of samples are taken, all samples shall be used in the analysis.  The landfill owner or operator shall divide the NMOC concentration from Method 25C by six to convert from CNMOC as carbon to CNMOC as hexane.

[NOTE: Test Methods found in Appendix A of 40 CFR 60 are incorporated by reference in ADEM Admin. Code R. 335-3-10-.03.]

(i) The landfill owner or operator shall recalculate the NMOC mass emission rate using the equations provided in subparagraph (a)1. or (a)1.(ii) of this paragraph and using the average NMOC concentration from the collected samples instead of the default value in the equation provided in subparagraph (a) of this paragraph.

(ii) If the resulting mass emission rate calculated using the site-specific NMOC concentration is equal to or greater than 50 megagrams per year, then the landfill owner or operator shall either comply with subparagraph (1)(b)2., or determine the site-specific methane generation rate constant and recalculate the NMOC emission rate using the site-specific methane generation rate using the procedure specified in subparagraph (a)4. of this paragraph below.

(iii) If the resulting NMOC mass emission rate is less than 50 megagrams per year, the owner or operator shall submit a periodic estimate of the emission rate report as provided in subparagraph (6)(b)1. of this Rule and retest the site-specific NMOC concentration every 5 years using the methods specified in this paragraph.

4. Tier 3. The site-specific methane generation rate constant shall be determined using the procedures provided in Method 2E of Appendix A. The landfill owner or operator shall estimate the NMOC mass emission rate using equations in subparagraph (a)1. or (a)1.(ii) of this paragraph and using a site-specific methane generation rate constant k, and the site-specific NMOC concentration as determined in subparagraph (a)3. of this paragraph instead of the default values provided in subparagraph (a) of this paragraph. The landfill owner or operator shall compare the resulting NMOC mass emission rate to the standard of 50 megagrams per year.

(i) If the NMOC mass emission rate as calculated using the site-specific methane generation rate and concentration of NMOC is equal to or greater than 50 megagrams per year, the owner or operator shall comply with subparagraph (1)(b)2. of this Rule.

(ii) If the NMOC mass emission rate is less than 50 megagrams per year, then the owner or operator shall submit a periodic emission rate report as provided in subparagraph (6)(b)1. of this Rule and shall recalculate the NMOC mass emission rate annually, as provided in subparagraph (6)(b)1. of this Rule using the equations in subparagraph (a) of this paragraph and using the site-specific methane generation rate constant and NMOC concentration obtained in subparagraph (a)3. of this paragraph. The calculation of the methane generation rate constant is performed only once, and the value obtained from this test shall be used in all subsequent annual NMOC emission rate calculations.

5. The owner or operator may use other methods to determine the NMOC concentration or a site-specific k as an alternative to the methods required in subparagraphs (a)3. and (a)4. of this paragraph if the method has been approved by the Administrator.

(b) After the installation of a collection and control system in compliance with paragraph (4) of this Rule, the owner or operator shall calculate the NMOC emission rate for purposes of determining when the system can be removed as provided in subparagraph (1)(b)2.(v) of this Rule, using the following equation:

where,

MNMOC 

= 

mass emission rate of NMOC, megagrams per year 

QLFG 

= 

flow rate of landfill gas, cubic meters per minute 

CNMOC 

= 

NMOC concentration, parts per million by volume as hexane 

1. The flow rate of landfill gas, QLFG, shall be determined by measuring the total landfill gas flow rate at the common header pipe that leads to the control device using a gas flow measuring device calibrated according to the provisions of Section 4 of Method 2E of Appendix A.

2. The average NMOC concentration, CNMOC, shall be determined by collecting and analyzing landfill gas sampled from the common header pipe before the gas moving or condensate removal equipment using the procedures in Method 25C or Method 18 of Appendix A. If using Method 18, the minimum list of compounds to be tested shall be those published in the most recent Compilation of Air Pollutant Emission Factors (AP-42). The sample location on the common header pipe shall be before any condensate removal or other gas refining units. The landfill owner or operator shall divide the NMOC concentration from Method 25C by six to convert from CNMOC as carbon to CNMOC as hexane.

3. The owner or operator may use another method to determine landfill gas flow rate and NMOC concentration if the method has been approved by the Director.

(c) When calculating emissions for PSD purposes, the owner or operator of each MSW landfill subject to the provisions of this Chapter shall estimate the NMOC emission rate for comparison to the PSD major source and significance levels in Rule 335-3-14-.04(2)(w) using AP-42 or other approved measurement procedures.

(d) For the performance test required in subparagraph (1)(b)2.(iii)(II), Method 25C or Method 18 shall be used to determine compliance with 98 weight-percent efficiency or the 20 ppmv outlet concentration level, unless another method to demonstrate compliance has been approved by the Director as provided by subparagraph (1)(b)2.(iii)(II). If using Method 18, the minimum list of compounds to be tested shall be those published in the most recent Compilation of Air Pollutant Emission Factors (AP-42). The following equation shall be used to calculate efficiency:

where,

NMOCin 

= 

mass of NMOC entering control device 

NMOCout 

= 

mass of NMOC exiting control device 

(4) Compliance Provisions.

(a) Except as provided in paragraph (1)(b)2.(i)(II) of this Rule, the specified methods in subparagraphs (a)1. through (a)6. of this paragraph shall be used to determine whether the gas collection system is in compliance with subparagraph (1)(b)2.(ii) of this Rule.

1. For the purposes of calculating the maximum expected gas generation flow rate from the landfill to determine compliance with subparagraph (1)(b)2.(ii)(I)I. of this Rule, one of the following equations shall be used. The k and Lo kinetic factors should be those published in the most recent Compilation of Air Pollutant Emission Factors (AP-42) or other site specific values demonstrated to be appropriate and approved by the Director. If k has been determined as specified in subparagraph (3)(a)4. of this Rule, the value of k determined from the test shall be used. A value of no more than 15 years shall be used for the intended use period of the gas mover equipment.  The active life of the landfill is the age of the landfill plus the estimated number of years until closure.

(i) For sites with unknown year-to-year solid waste acceptance rate:

where,

Qm 

= 

maximum expected gas generation flow rate, cubic meters per year 

Lo 

= 

methane generation potential, cubic meters per megagram solid waste 

R 

= 

average annual acceptance rate, megagrams per year 

k 

= 

methane generation rate constant, year-1 

t 

= 

age of the landfill at equipment installation plus the time the owner or operator intends to use the gas mover equipment or active life of the landfill, whichever is less.  If the equipment is installed after closure, t is the age of the landfill at installation, years 

c 

= 

time since closure, years (for an active landfill c = 0 and e-kc = 1) 

(ii) For sites with known year-to-year solid waste acceptance rate:

where,

Qm 

= 

maximum expected gas generation flow rate, cubic meters per year 

k 

= 

methane generation rate constant, year-1 

Lo 

= 

methane generation potential, cubic meters per megagram solid waste 

Mi 

= 

mass of solid waste in the ith section, megagrams 

ti 

= 

age of the ith section, years 

(iii) If a collection and control system has been installed, actual flow data may be used to project the maximum expected gas generation flow rate instead of, or in conjunction with, the equations in subparagraphs (a)1.(i) and (ii) of this paragraph.  If the landfill is still accepting waste, the actual measured flow data will not equal the maximum expected gas generation rate, so calculations using the equations in subparagraphs (a)1.(i) or (ii) or other methods shall be used to predict the maximum expected gas generation rate over the intended period of use of the gas control system equipment.

2. For the purposes of determining sufficient density of gas collectors for compliance with subparagraph (1)(b)2.(ii)(I)II., the owner or operator shall design a system of vertical wells, horizontal collectors, or other collection devices, satisfactory to the Director, capable of controlling and extracting gas from all portions of the landfill sufficient to meet all operational and performance standards.

3. For the purpose of demonstrating whether the gas collection system flow rate is sufficient to determine compliance with subparagraph (1)(b)2.(ii)(I)III. of this Rule, the owner or operator shall measure gauge pressure in the gas collection header at each individual well, monthly. If a positive pressure exists, action shall be initiated to correct the exceedance within 5 calendar days, except for the three conditions allowed under subparagraph (2)(b) of this Rule.  If negative pressure cannot be achieved without excess air infiltration within 15 calendar days of the first measurement, the gas collection system shall be expanded to correct the exceedance within 120 days of the initial measurement of positive pressure. Any attempted corrective measure shall not cause exceedances of other operational or performance standards. An alternative timeline for correcting the exceedance may be submitted to the Director for approval.

4. Owners or operators are not required to expand the system as required in subparagraph (a)3. of this paragraph during the first 180 days after gas collection system start-up.

5. For the purpose of identifying whether excess air infiltration into the landfill is occurring, the owner or operator shall monitor each well monthly for temperature and nitrogen or oxygen as provided in subparagraph (2)(c) of this Rule. If a well exceeds one of these operating parameters, action shall be initiated to correct the exceedance within 5 calendar days. If correction of the exceedance cannot be achieved within 15 calendar days of the first measurement, the gas collection system shall be expanded to correct the exceedance within 120 days of the initial exceedance. Any attempted corrective measure shall not cause exceedances of other operational or performance standards. An alternative timeline for correcting the exceedance may be submitted to the Director for approval.

6. An owner or operator seeking to demonstrate compliance with subparagraph (1)(b)2.(ii)(I)IV. of this Rule through the use of a collection system not conforming to the specifications provided in paragraph (8) of this Rule shall provide information satisfactory to the Director as specified in subparagraph (1)(b)2.(i)(III) of this Rule demonstrating that off-site migration is being controlled.

(b) For purposes of compliance with subparagraph (2)(a) of this Rule, each owner or operator of a controlled landfill shall place each well or design component as specified in the approved design plan as provided in subparagraph (1)(b)2.(i). Each well shall be installed no later than 60 days after the date on which the initial solid waste has been in place for a period of:

1. 5 years or more if active; or

2. 2 years or more if closed or at final grade.

(c) The following procedures shall be used for compliance with the surface methane operational standard as provided in subparagraph (2)(d) of this Rule.

1. After installation of the collection system, the owner or operator shall monitor surface concentrations of methane along the entire perimeter of the collection area and along a pattern that traverses the landfill at 30 meter intervals (or a site-specific established spacing) for each collection area on a quarterly basis using an organic vapor analyzer, flame ionization detector, or other portable monitor meeting the specifications provided in subparagraph (d) of this paragraph.

2. The background concentration shall be determined by moving the probe inlet upwind and downwind outside the boundary of the landfill at a distance of at least 30 meters from the perimeter wells.

3. Surface emission monitoring shall be performed in accordance with Section 4.3.1 of Method 21 of Appendix A, except that the probe inlet shall be placed within 5 to 10 centimeters of the ground. Monitoring shall be performed during typical meteorological conditions.

4. Any reading of 500 parts per million or more above background at any location shall be recorded as a monitored exceedance and the actions specified in subparagraphs (c)4.(i) through (v) of this paragraph below shall be taken. As long as the specified actions are taken, the exceedance is not a violation of the operational requirements of subparagraph (2)(d) of this Rule.

(i) The location of each monitored exceedance shall be marked and the location recorded.

(ii) Cover maintenance or adjustments to the vacuum of the adjacent wells to increase the gas collection in the vicinity of each exceedance shall be made and the location shall be re-monitored within 10 calendar days of detecting the exceedance.

(iii) If the re-monitoring of the location shows a second exceedance, additional corrective action shall be taken and the location shall be monitored again within 10 days of the second exceedance. If the re-monitoring shows a third exceedance for the same location, the action specified in subparagraph (c)4.(v) of this paragraph shall be taken, and no further monitoring of that location is required until the action specified in subparagraph (c)4.(v) has been taken.

(iv) Any location that initially showed an exceedance but has a methane concentration less than 500 ppm methane above background at the 10-day re-monitoring specified in subparagraph (c)4.(ii) or (iii) of this paragraph shall be re-monitored 1 month from the initial exceedance. If the 1-month remonitoring shows a concentration less than 500 parts per million above background, no further monitoring of that location is required until the next quarterly monitoring period. If the 1-month remonitoring shows an exceedance, the actions specified in subparagraph (c)4.(iii) or (v) of this paragraph shall be taken.

(v) For any location where monitored methane concentration equals or exceeds 500 parts per million above background three times within a quarterly period, a new well or other collection device shall be installed within 120 calendar days of the initial exceedance.  An alternative remedy to the exceedance, such as upgrading the blower, header pipes or control device, and a corresponding timeline for installation may be submitted to the Director for approval.

5. The owner or operator shall implement a program to monitor for cover integrity and implement cover repairs as necessary on a monthly basis.

(d) Each owner or operator seeking to comply with the provisions in paragraph (c) of this paragraph shall comply with the following instrumentation specifications and procedures for surface emission monitoring devices:

1. The portable analyzer shall meet the instrument specifications provided in Section 3 of Method 21 of Appendix A, except that "methane" shall replace all references to VOC.

2. The calibration gas shall be methane, diluted to a nominal concentration of 500 parts per million in air.

3. To meet the performance evaluation requirements in Section 3.1.3 of Method 21 of Appendix A, the instrument evaluation procedures of Section 4.4 of Method 21 of Appendix A shall be used.

4. The calibration procedures provided in Section 4.2 of Method 21 of Appendix A shall be followed immediately before commencing a surface monitoring survey.

(e) The provisions of this paragraph apply at all times, except during periods of start-up, shutdown, or malfunction, provided that the duration of start-up, shutdown, or malfunction shall not exceed 5 days for collection systems and shall not exceed 1 hour for treatment or control devices.

(5) Monitoring of Operations. Except as provided in subparagraph (1)(b)2.(i)(II) of this Rule,

(a) Each owner or operator seeking to comply with subparagraph (1)(b)2.(ii)(I) of this Rule for an active gas collection system shall install a sampling port and a thermometer, other temperature measuring device, or an access port for temperature measurements at each wellhead and:

1. Measure the gauge pressure in the gas collection header on a monthly basis as provided in subparagraph (4)(a)3. of this Rule; and

2. Monitor nitrogen or oxygen concentration in the landfill gas on a monthly basis as provided in subparagraph (4)(a)5. of this Rule; and

3. Monitor temperature of the landfill gas on a monthly basis as provided in subparagraph (4)(a)5. of this Rule.

(b) Each owner or operator seeking to comply with subparagraph (1)(b)2.(iii) of this Rule using an enclosed combustor shall calibrate, maintain, and operate according to the manufacturer's specifications, the following equipment.

1. A temperature monitoring device equipped with a continuous recorder and having a minimum accuracy of ±1 percent of the temperature being measured expressed in ºCelsius or ±0.5 ºC, whichever is greater. A temperature monitoring device is not required for boilers or process heaters with design heat input capacity equal to or greater than 44 megawatts.

2. A device that records flow to or bypass of the control device. The owner or operator shall either:

(i) Install, calibrate, and maintain a gas flow rate measuring device that shall record the flow to the control device at least every 15 minutes; or

(ii) Secure the bypass line valve in the closed position with a car-seal or a lock-and-key type configuration. A visual inspection of the seal or closure mechanism shall be performed at least once every month to ensure that the valve is maintained in the closed position and that the gas flow is not diverted through the bypass line.

(c) Each owner or operator seeking to comply with subparagraph (b)2.(iii) of this Rule using an open flare shall install, calibrate, maintain, and operate according to the manufacturer's specifications the following equipment:

1. A heat sensing device, such as an ultraviolet beam sensor or thermocouple, at the pilot light or the flame itself to indicate the continuous presence of a flame.

2. A device that records flow to or bypass of the flare. The owner or operator shall either:

(i) Install, calibrate, and maintain a gas flow rate measuring device that shall record the flow to the control device at least every 15 minutes; or

(ii) Secure the bypass line valve in the closed position with a car-seal or a lock-and-key type configuration. A visual inspection of the seal or closure mechanism shall be performed at least once every month to ensure that the valve is maintained in the closed position and that the gas flow is not diverted through the bypass line.

(d) Each owner or operator seeking to demonstrate compliance with subparagraph (1)(b)2.(iii) of this Rule using a device other than an open flare or an enclosed combustor shall provide information satisfactory to the Director as provided in subparagraph (1)(b)2.(i)(II) of this Rule describing the operation of the control device, the operating parameters that would indicate proper performance, and appropriate monitoring procedures. The Director shall review the information and either approve it, or request that additional information be submitted. The Director may specify additional appropriate monitoring procedures.

(e) Each owner or operator seeking to install a collection system that does not meet the specifications in paragraph (8) of this Rule or seeking to monitor alternative parameters to those required by paragraphs (2) through (5) of this Rule shall provide information satisfactory to the Director as provided in subparagraphs (1)(b)2.(i)(II) and (III) of this Rule describing the design and operation of the collection system, the operating parameters that would indicate proper performance, and appropriate monitoring procedures. The Director may specify additional appropriate monitoring procedures.

(f) Each owner or operator seeking to demonstrate compliance with subparagraph (4)(c) of this Rule, shall monitor surface concentrations of methane according to the instrument specifications and procedures provided in subparagraph (4)(d) of this Rule. Any closed landfill that has no monitored exceedances of the operational standard in three consecutive quarterly monitoring periods may skip to annual monitoring. Any methane reading of 500 ppm or more above background detected during the annual monitoring returns the frequency for that landfill to quarterly monitoring.

(6) Reporting Requirements. Except as provided in subparagraph (1)(b)2.(i)(II) of this Rule,

(a) Each owner or operator subject to the requirements of this Chapter shall submit an initial design capacity report to the Director.

1. The initial design capacity report shall fulfill the requirements of the notification of the date construction is commenced as required under §60.7(a)(1), 40 CFR and shall be submitted no later than 90 days from the effective date of these Rules.

2. The initial design capacity report shall contain the following information:

(i) A map or plot of the landfill, providing the size and location of the landfill, and identifying all areas where solid waste may be landfilled according to the provisions of the State permit;

(ii) The maximum design capacity of the landfill. Where the maximum design capacity is specified in the State permit, a copy of the permit specifying the maximum design capacity may be submitted as part of the report. If the maximum design capacity of the landfill is not specified in the permit, the maximum design capacity shall be calculated using good engineering practices. The calculations shall be provided, along with the relevant parameters as part of the report. The Director may request other reasonable information as may be necessary to verify the maximum design capacity of the landfill.

3. An amended design capacity report shall be submitted to the Director providing notification of any increase in the design capacity of the landfill, within 90 days of an increase in the maximum design capacity of the landfill to or above 2.5 million megagrams and 2.5 million cubic meters. This increase in design capacity may result from an increase in the permitted volume of the landfill or an increase in the density as documented in the annual recalculation required in subparagraph (7)(f) of this Rule.

(b) Each owner or operator subject to the requirements of this Chapter shall submit an NMOC emission rate report to the Director initially and annually thereafter, except as provided for in subparagraphs (b)1.(ii) or (b)3. of this paragraph. The Director may request such additional information as may be necessary to verify the reported NMOC emission rate.

1. The NMOC emission rate report shall contain an annual or 5-year estimate of the NMOC emission rate calculated using the formula and procedures provided in subparagraphs (3)(a) or (b) of this Rule, as applicable.

(i) The initial NMOC emission rate report shall be submitted within 90 days from the effective date of these Rules and may be combined with the initial design capacity report required in subparagraph (a) of this paragraph. Subsequent NMOC emission rate reports shall be submitted annually thereafter, except as provided for in subparagraphs (b)1.(ii) and (b)3. of this paragraph.

(ii) If the estimated NMOC emission rate as reported in the annual report to the Director is less than 50 megagrams per year in each of the next 5 consecutive years, the owner or operator may elect to submit an estimate of the NMOC emission rate for the next 5-year period in lieu of the annual report. This estimate shall include the current amount of solid waste-in-place and the estimated waste acceptance rate for each year of the 5 years for which an NMOC emission rate is estimated. All data and calculations upon which this estimate is based shall be provided to the Director. This estimate shall be revised at least once every 5 years. If the actual waste acceptance rate exceeds the estimated waste acceptance rate in any year reported in the 5-year estimate, a revised 5-year estimate shall be submitted to the Director. The revised estimate shall cover the 5-year period beginning with the year in which the actual waste acceptance rate exceeded the estimated waste acceptance rate.

2. The NMOC emission rate report shall include all the data, calculations, sample reports and measurements used to estimate the annual or 5-year emissions.

3. Each owner or operator subject to the requirements of this Chapter is exempted from the requirements of subparagraphs (b)1. and 2. of this paragraph, after the installation of a collection and control system in compliance with subparagraph (1)(b)2. of this Rule, during such time as the collection and control system is in operation and in compliance with paragraphs (2) and (4) of this Rule.

(c) Each owner or operator subject to the provisions of subparagraph (1)(b)2.(i) of this Rule shall submit a collection and control system design plan to the Director within 1 year of the first report, required under subparagraph (b) of this paragraph, in which the emission rate equal to or exceeds 50 megagrams per year, except as follows:

1. If the owner or operator elects to recalculate the NMOC emission rate after Tier 2 NMOC sampling and analysis as provided in subparagraph (3)(a)3. of this Rule and the resulting rate is less than 50 megagrams per year, annual periodic reporting shall be resumed, using the Tier 2 determined site-specific NMOC concentration, until the calculated emission rate is equal to or greater than 50 megagrams per year or the landfill is closed. The revised NMOC emission rate report, with the recalculated emission rate based on NMOC sampling and analysis, shall be submitted within 180 days of the first calculated exceedance of 50 megagrams per year.

2. If the owner or operator elects to recalculate the NMOC emission rate after determining a site-specific methane generation rate constant (k), as provided in Tier 3 in subparagraph (3)(a)4. of this Rule, and the resulting NMOC emission rate is less than 50 Mg/yr, annual periodic reporting shall be resumed. The resulting site-specific methane generation rate constant (k) shall be used in the emission rate calculation until such time as the emissions rate calculation results in an exceedance. The revised NMOC emission rate report based on the provisions of subparagraph (3)(a)4. of this Rule and the resulting site-specific methane generation rate constant (k) shall be submitted to the Director within 1 year of the first calculated emission rate exceeding 50 megagrams per year.

(d) Each owner or operator of a controlled landfill shall submit a closure report to the Director within 30 days of waste acceptance cessation. The Director may request additional information as may be necessary to verify that permanent closure has taken place in accordance with the requirements of ADEM Admin. Code Chapter 335-13-4. If a closure report has been submitted to the Director, no additional wastes may be placed into the landfill without filing a notification of modification as described under §60.7(a)(4), 40 CFR.

(e) Each owner or operator of a controlled landfill shall submit an equipment removal report to the Director 30 days prior to removal or cessation of operation of the control equipment.

1. The equipment removal report shall contain all of the following items:

(i) A copy of the closure report submitted in accordance with paragraph (d) of this paragraph;

(ii) A copy of the initial performance test report demonstrating that the 15 year minimum control period has expired; and

(iii) Dated copies of three successive NMOC emission rate reports demonstrating that the landfill is no longer producing 50 megagrams or greater of NMOC per year.

2. The Director may request such additional information as may be necessary to verify that all of the conditions for removal in subparagraph (1)(b)2.(v) of this Rule have been met.

(f) Each owner or operator of a landfill seeking to comply with subparagraph (1)(b)2. of this Rule using an active collection system designed in accordance with subparagraph (1)(b)2.(ii) of this Rule shall submit to the Director annual reports of the recorded information in subparagraphs (f)1. through (f)6. of this paragraph. The initial annual report shall be submitted within 180 days of installation and start-up of the collection and control system, and shall include the initial performance test report required under §60.8, 40 CFR. For enclosed combustion devices and flares, reportable exceedances are defined under subparagraph (7)(c) of this Rule.

1. Value and length of time for exceedance of applicable parameters monitored under subparagraphs (5)(a), (b), (c), and (d) of this Rule.

2. Description and duration of all periods when the gas stream is diverted from the control device through a bypass line or the indication of bypass flow as specified under paragraph (5) of this Rule.

3. Description and duration of all periods when the control device was not operating for a period exceeding 1 hour and length of time the control device was not operating.

4. All periods when the collection system was not operating in excess of 5 days.

5. The location of each exceedance of the 500 parts per million methane concentration as provided in subparagraph (2)(d) of this Rule and the concentration recorded at each location for which an exceedance was recorded in the previous month.

6. The date of installation and the location of each well or collection system expansion added pursuant to subparagraphs (a)3., (b), and (c)4. of paragraph (4).

(g) Each owner or operator seeking to comply with subparagraph (1)(b)2.(i) of this Rule shall include the following information with the initial performance test report required under §60.8, 40 CFR:

1. A diagram of the collection system showing collection system positioning including all wells, horizontal collectors, surface collectors, or other gas extraction devices, including the locations of any areas excluded from collection and the proposed sites for the future collection system expansion;

2. The data upon which the sufficient density of wells, horizontal collectors, surface collectors, or other gas extraction devices and the gas mover equipment sizing are based;

3. The documentation of the presence of asbestos or nondegradable material for each area from which collection wells have been excluded based on the presence of asbestos or nondegradable material;

4. The sum of the gas generation flow rates for all areas from which collection wells have been excluded based on nonproductivity and the calculations of gas generation flow rate for each excluded area; and

5. The provisions for increasing gas mover equipment capacity with increased gas generation flow rate, if the present gas mover equipment is inadequate to move the maximum flow rate expected over the life of the landfill; and

6. The provisions for the control of off-site migration.

(7) Recordkeeping Requirements.

(a) Except as provided in subparagraph (1)(b)2.(i)(II) of this Rule, each owner or operator of an MSW landfill subject to the provisions of subparagraph (1)(b) of this Rule shall keep for at least 5 years up-to-date, readily accessible, on-site records of the design capacity report which triggered subparagraph (1)(b), the current amount of solid waste in-place, and the year-by-year waste acceptance rate. Off-site records may be maintained if they are retrievable within 4 hours.  Either paper copy or electronic formats are acceptable.

(b) Except as provided in subparagraph (1)(b)2.(i)(II) of this Rule, each owner or operator of a controlled landfill shall keep up-to-date, readily accessible records for the life of the control equipment of the data listed in subparagraphs (b)1. through (b)4. of this paragraph as measured during the initial performance test or compliance determination. Records of subsequent tests or monitoring shall be maintained for a minimum of 5 years. Records of the control device vendor specifications shall be maintained until removal.

1. Where an owner or operator subject to the provisions of this Chapter seeks to demonstrate compliance with subparagraph (1)(b)2.(ii) of this Rule:

(i) The maximum expected gas generation flow rate as calculated in subparagraph (4)(a)1. of this Rule. The owner or operator may use another method to determine the maximum gas generation flow rate, if the method has been approved by the Director.

(ii) The density of wells, horizontal collectors, surface collectors, or other gas extraction devices determined using the procedures specified in subparagraph (8)(a)1. of this Rule.

2. Where an owner or operator subject to the provisions of this Chapter seeks to demonstrate compliance with subparagraph (1)(b)2.(iii) of this Rule through use of an enclosed combustion device other than a boiler or process heater with a design heat input capacity equal to or greater than 44 megawatts:

(i) The average combustion temperature measured at least every 15 minutes and averaged over the same time period of the performance test.

(ii) The percent reduction of NMOC determined as specified in subparagraph (1)(b)2.(iii)(II) of this paragraph achieved by the control device.

3. Where an owner or operator subject to the provisions of this Chapter seeks to demonstrate compliance with subparagraph (1)(b)2.(iii)(II)I. of this Rule through use of a boiler or process heater of any size: a description of the location at which the collected gas vent stream is introduced into the boiler or process heater over the same time period of the performance testing.

4. Where an owner or operator subject to the provisions of this Chapter seeks to demonstrate compliance with subparagraph (1)(b)2.(iii)(I) of this Rule through use of an open flare, the flare type (i.e., steam-assisted, air-assisted, or nonassisted), all visible emission readings, heat content determination, flow rate or bypass flow rate measurements, and exit velocity determinations made during the performance test as specified in §60.18, 40 CFR; continuous records of the flare pilot flame or flare flame monitoring and records of all periods of operations during which the pilot flame of the flare flame is absent.

(c) Except as provided in subparagraph (1)(b)2.(i)(II) of this Rule, each owner or operator of a controlled landfill subject to the provisions of this Chapter shall keep for 5 years up-to-date, readily accessible continuous records of the equipment operating parameters specified to be monitored in paragraph (5) of this Rule as well as up-to-date, readily accessible records for periods of operation during which the parameter boundaries established during the most recent performance test are exceeded.

1. The following constitute exceedances that shall be recorded and reported under subparagraph (6)(f) of this Rule:

(i) For enclosed combustors except for boilers and process heaters with design heat input capacity of 44 megawatts (150 million British thermal unit per hour) or greater, all 3-hour periods of operation during which the average combustion temperature was more than 28 ºC below the average combustion temperature during the most recent performance test at which compliance with subparagraph (1)(b)2.(iii) of this Rule was determined.

(ii) For boilers or process heaters, whenever there is a change in the location at which the vent stream is introduced into the flame zone as required under subparagraph (b)3. of this paragraph.

2. Each owner or operator subject to the provisions of this Chapter shall keep up-to-date, readily accessible continuous records of the indication of flow to the control device or the indication of bypass flow or records of monthly inspections of car-seals or lock-and-key configurations used to seal bypass lines, specified under paragraph (5) of this Rule.

3. Each owner or operator subject to the provisions of this Chapter who uses a boiler or process heater with a design heat input capacity of 44 megawatts or greater to comply with subparagraph (1)(b)2.(iii) shall keep an up-to-date, readily accessible record of all periods of operation of the boiler or process heater.  (Examples of such records could include records of steam use, fuel use, or monitoring data collected pursuant to other State regulatory requirements.)

4. Each owner or operator seeking to comply with the provisions of this Chapter by use of an open flare shall keep up-to-date, readily accessible continuous records of the flame or flare pilot flame monitoring specified under subparagraph (5)(c) of this Rule, and up-to-date, readily accessible records of all periods of operation in which the flame or flare pilot flame is absent.

(d) Except as provided in subparagraph (1)(b)2.(i)(II) of this Rule, each owner or operator subject to the provisions of this Chapter shall keep for the life of the collection system an up-to-date, readily accessible plot map showing each existing and planned collector in the system and providing a unique identification location label for each collector.

1. Each owner or operator subject to the provisions of this Chapter shall keep up-to-date, readily accessible records of the installation date and location of all newly installed collectors as specified under subparagraph (4)(b) of this Rule.

2. Each owner or operator subject to the provisions of this Chapter shall keep readily accessible documentation of the nature, date of deposition, amount, and location of asbestos-containing or nondegradable waste excluded from collection as provided in subparagraph (8)(a)3.(i) of this Rule as well as any nonproductive areas excluded from collection as provided in subparagraph (8)(a)3.(ii) of this Rule.

(e) Except as provided in subparagraph (1)(b)2.(i)(II) of this Rule, each owner or operator subject to the provisions of this Chapter shall keep for at least 5 years up-to-date, readily accessible records of all collection and control system exceedances of the operational standards in paragraph (2) of this Rule, the reading in the subsequent month whether or not the second reading is an exceedance, and the location of each exceedance.

(f) Landfill owners or operators who convert design capacity from volume to mass or mass to volume to demonstrate that landfill design capacity is less than 2.5 million megagrams or 2.5 million cubic meters, as provided in the definition of "design capacity", shall keep readily accessible, on-site records of the annual recalculation of site-specific density, design capacity, and the supporting documentation. Off-site records may be maintained if they are retrievable within 4 hours. Either paper copy or electronic format are acceptable.

(8) Specifications for Active Collection Systems.

(a) Each owner or operator seeking to comply with subparagraph (1)(b)2.(i) of this Rule shall site active collection wells, horizontal collectors, surface collectors, or other extraction devices at a sufficient density throughout all gas producing areas using the following procedures unless alternative procedures have been approved by the Director as provided in subparagraphs (1)(b)2.(i)(III) and (IV) of this Rule:

1. The collection devices within the interior and along the perimeter areas shall be certified to achieve comprehensive control of surface gas emissions by a professional engineer. The following issues shall be addressed in the design: depths of refuse, refuse gas generation rates and flow characteristics, cover properties, gas system expandability, leachate and condensate management, accessibility, compatibility with filling operations, integration with closure end use, air intrusion control, corrosion resistance, fill settlement, and resistance to the refuse decomposition heat.

2. The sufficient density of gas collection devices determined in subparagraph (a)1. of this paragraph shall address landfill gas migration issues and augmentation of the collection system through the use of active or passive systems at the landfill perimeter or exterior.

3. The placement of gas collection devices determined in subparagraph (a)1. of this paragraph shall control all gas producing areas, except as provided by subparagraphs (a)3.(i) and (a)3.(ii) of this paragraph.

(i) Any segregated area of asbestos or nondegradable material may be excluded from collection if documented as provided under subparagraph (7)(d) of this Rule.  The documentation shall provide the nature, date of deposition, location and amount of asbestos or nondegradable material deposited in the area, and shall be provided to the Director upon request.

(ii) Any nonproductive area of the landfill may be excluded from control, provided that the total of all excluded areas can be shown to contribute less than 1 percent of the total amount of NMOC emissions from the landfill. The amount, location, and age of the material shall be documented and provided to the Director upon request. A separate NMOC emissions estimate shall be made for each section proposed for exclusion, and the sum of all such sections shall be compared to the NMOC emissions estimate for the entire landfill. Emissions from each section shall be computed using the following equation:

where,

Qi 

= 

NMOC emission rate from the ith section, megagrams per year 

k 

= 

methane generation rate constant, year-1 

Lo 

= 

methane generation potential, cubic meters per megagram solid waste 

Mi 

= 

mass of the degradable solid waste in the ith section, megagram 

ti 

= 

age of the solid waste in the ith section, years 

CNMOC 

= 

concentration of nonmethane organic compounds, parts per million by volume 

3.6 x 10-9 

= 

conversion factor 

(iii) The values for k, and CNMOC determined in field testing shall be used, if field testing has been performed in determining the NMOC emission rate or the radii of influence (the distance from the well center to a point in the landfill where the pressure gradient applied by the blower or compressor approaches zero). If field testing has not been performed, the default values for k, Lo and CNMOC provided in subparagraph (3)(a) of this Rule or the alternative values from subparagraph (3)(a)5. of this Rule shall be used. The mass of nondegradable solid waste contained within the given section may be subtracted from the total mass of the section when estimating emissions provided the nature, location, age, and amount of the nondegradable material is documented as provided in subparagraph (a)3.(i) of this paragraph.

(b) Each owner or operator seeking to comply with subparagraph (1)(b)2.(i)(I) of this Rule shall construct the gas collection devices using the following equipment or procedures:

1. The landfill gas extraction components shall be constructed of polyvinyl chloride (PVC), high density polyethylene (HDPE) pipe, fiberglass, stainless steel, or other nonporous corrosion resistant material of suitable dimensions to: convey projected amounts of gases; withstand installation, static, and settlement forces; and withstand planned overburden or traffic loads. The collection system shall extend as necessary to comply with emission and migration standards. Collection devices such as wells and horizontal collectors shall be perforated to allow gas entry without head loss sufficient to impair performance across the intended extent of control. Perforations shall be situated with regard to the need to prevent excessive air infiltration.

2. Vertical wells shall be placed so as not to endanger underlying liners and shall address the occurrence of water within the landfill. Holes and trenches constructed for piped wells and horizontal collectors shall be of sufficient cross-section so as to allow for their proper construction and completion including, for example, centering of pipes and placement of gravel backfill. Collection devices shall be designed so as not to allow indirect short circuiting of air into the cover or refuse into the collection system or gas into the air. Any gravel used around pipe perforations should be of a dimension so as not to penetrate or block perforations.

3. Collection devices may be connected to the collection header pipes below or above the landfill surface. The connector assembly shall include a positive closing throttle valve, any necessary seals and couplings, access couplings and at least one sampling port. The collection devices shall be constructed of PVC, HDPE, fiberglass, stainless steel, or other nonporous material of suitable thickness.

(c) Each owner or operator seeking to comply with subparagraph (1)(b)2.(i)(I) of this Rule shall convey the landfill gas to a control system in compliance with subparagraph (1)(b)2.(iii) of this Rule through the collection header pipe(s). The gas mover equipment shall be sized to handle the maximum gas generation flow rate expected over the intended use period of the gas moving equipment using the following procedures:

1. For existing collection systems, the flow data shall be used to project the maximum flow rate. If no flow data exists, the procedures in subparagraph (c)2. of this paragraph shall be used.

2. For new collection systems, the maximum flow rate shall be in accordance with subparagraph (4)(a)1. of this Rule.

Author: Ronald W. Gore

Statutory Authority: Code of Ala. 1975, §§22-28-14, 22-22A-5, 22-22A-6, 22-22A-8.

History: New Rule: Filed December 11, 1997; effective January 15, 1998. Amended: Filed December 9, 1999; effective January 13, 2000. Amended: Filed August 3, 2000; effective September 7, 2000. Amended: Filed February 7, 2002; effective March 14, 2002.

335-3-19-.04 Compliance Schedules.

(1) Except as provided for under paragraph (2) of this Rule, planning, awarding of contracts, and installation of MSW landfill air emission collection and control equipment capable of meeting the emission standards established under this Chapter, shall be accomplished within 30 months after the date the initial NMOC emission rate report shows NMOC emissions equal or exceed 50 megagrams per year.

(2) For each existing MSW landfill meeting the conditions in Rules 335-3-19-.02(2)(a) and (2)(b) whose NMOC emission rate is less than 50 megagrams per year on the effective date of Rule 335-3-19-.03, installation of collection and control systems capable of meeting emission standards established under this Chapter shall be accomplished within 30 months of the date when the condition in Rule 335-3-19-.02(2)(c) is met (i.e., the date of the first annual nonmethane organic compounds emission rate which equals or exceeds 50 megagrams per year).

Author: Ronald W. Gore

Statutory Authority: Code of Ala. 1975, §§22-28-14, 22-22A-5, 22-22A-6, 22-22A-8.

History: New Rule: Filed December 11, 1997; effective January 15, 1998. Amended: Filed December 9, 1999; effective January 13, 2000.

335-3-19-.05 Petition For Alternative Standards And Compliance Schedules.

(1) A MSW landfill owner or operator may request through petition, alternative emission standards or a longer compliance schedule that is/are not specified in this Chapter through the following procedures.

(a) Petition Requirements. To enable the Department to rule on the Petition, the following information, where determined applicable by the Department, shall be included in the petition:

1. A clear and complete statement of the precise extent of the relief sought including specific identification of the particular provisions of the regulations from which the petition is sought. The criteria for relief include:

(i) Unreasonable cost of control resulting from landfill age, location, or basic design:

(ii) Physical impossibility of installing necessary control equipment; or

(iii) Other factors specific to the landfill that make application of a less stringent standard or final compliance time significantly more reasonable.

(2) An assessment, with supporting factual information, of the impact that the petition will impose on the public health and the environment in the affected area.

(3) Any additional information requested by the Department as necessary to evaluate the petition.

(4) A concise factual statement of the reasons the petitioner believes that alternative emission limits or a longer compliance schedule will not threaten the public health or unreasonably create environmental pollution.

(b) Extension of Prior or Existing Alternative Emission Standards or Compliance Schedule. A petition to extend a prior or existing petition granted by the Department shall be commenced by filing a new petition with the Department in accordance with the requirements of paragraph (1) of this Rule. To the extent that the information required by paragraph (1) of this Rule has been included in the prior petition for which extension is sought, a submission of that information shall not be required provided that the petition shall request the incorporation of the record, opinion and order in the prior proceeding into the new petition.

(c) Department Actions on Petitions. On receipt of a petition, the Department will authorize one of the following actions, as they shall determine:

1. The petition may be dismissed if the Department determines that it is not adequate under paragraph (1) of this Rule.

2. The Department may grant the request of the petition, as petitioned or by imposing such conditions as this Division may require in the Major Source Operating Permit, including the establishment of schedules of compliance and monitoring requirements, if EPA consents to the extension of prior or existing alternative emission standards or compliance schedule as submitted to EPA by the Department.

3. The Department may deny the petition. If such a denial is made, the Department shall notify the petitioner in writing, the reasons for denial and outline procedures for appeal.

(d) Termination Procedures. Any petition granted by the Department may be terminated by the Department whenever the Department finds, after an opportunity for the petitioner to demonstrate compliance and after notice and an opportunity for hearing, that the petitioner is in violation of any requirement, condition, schedule, limitation or any other provision of the petition or that operation under the petition does not meet the minimum requirements established by state and federal laws and regulations or is unreasonably threatening the public health.

Author: Ronald W. Gore

Statutory Authority: Code of Ala. 1975, §§22-28-14, 22-22A-5, 22-22A-6, 22-22A-8.

History: New Rule: Filed December 11, 1997; effective January 15, 1998. Amended: Filed August 3, 2000; effective September 7, 2000.