[37 Pa.B. 1662]
[Saturday, April 14, 2007]
[Continued from previous Web Page] 76. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the total combined PM emissions from the DDGS loadout operation, including fugitive PM emissions, shall not exceed 0.45 ton in any 12-consecutive month period.
77. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the total combined PM10 emissions from the DDGS loadout operation, including fugitive PM10 emissions, shall not exceed 0.24 ton in any 12-consecutive month period.
78. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the DDGS storage building shall be a total enclosure which shall be maintained under negative pressure by the DDGS loadout fabric collector at all times that DDGS is being transferred into or stored within the building.
79. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the DDGS loadout fabric collector shall capture, at a minimum, 50% of the PM and PM10 generated from the DDGS loadout operation.
80. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, all truck or railcar hatches and openings that are not in actual use for DDGS loading shall be closed during loading operations.
81. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, if it is determined by the Department that the aspirated loadout spouts incorporated in the DDGS loadout operation do not provide adequate PM and/or PM10 control during the loading of railcars, the company shall add flexible boots around the loadout spouts that provide a seal over the top hatch of the railcars being loaded.
82. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, all conveyors associated with the DDGS loadout operation shall be fully enclosed.
83. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the facility shall load out no more than 339,100 tons of DDGS in any 12-consecutive month period. Records shall be maintained of the amount of DDGS loaded out during each month. All records generated under this condition shall be retained for at least 5 years and shall be made available to the Department upon request.
84. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall submit semi-annual reports to the Department listing the amount of DDGS loaded out during each month of the respective reporting period. Each semi-annual report shall be submitted to the Department by no later than September 1 (for the immediately-preceding January 1 through June 30 period) and March 1 (for the immediately-preceding July 1 through December 31 period).
85. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, all of the wetcake loadout structure's potential openings shall remain closed during loadout and the wetcake loadout structure shall be maintained under negative pressure and vented to the CFB boiler.
86. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the VOC collection system associated with the wetcake loadout operation shall have a minimum capture efficiency of 95%.
87. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the total combined fugitive VOC emissions from the wetcake loadout operation shall not exceed 0.22 ton in any 12-consecutive month period.
88. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, wetcake shall only be loaded into trucks that are completely contained within the structure during loadout operations.
89. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the facility shall load out no more than 1,059,783 tons of wetcake in any 12-consecutive month period. Records shall be maintained of the amount of wetcake loaded out during each month. All records generated under this condition shall be retained for at least 5 years and shall be made available to the Department upon request.
90. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall submit semi-annual reports to the Department listing the amount of wetcake loaded out during each month of the respective reporting period. Each semi-annual report shall be submitted to the Department by no later than September 1 (for the immediately-preceding January 1 through June 30 period) and March 1 (for the immediately-preceding July 1 through December 31 period).
91. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the ethanol loadout operation shall be controlled by an enclosed flare which shall maintain a combustion chamber temperature of at least 1,600° F (for a retention time of at least 0.75 second) any time VOCs or volatile HAPs are being ducted to it. Within 30 days of the selection of the specific flare the permittee proposes to install, the permittee shall notify the Department of the manufacturer and model of the specific flare selected and shall additionally, at the same time, submit to the Department for review specifications for the flare that are comprehensive enough to allow the Department to determine if the selected flare is equivalent to that proposed in the plan approval application.
92. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the enclosed flare shall achieve a VOC and volatile HAP destruction efficiency of no less than 98% at all times VOCs or volatile HAPs are being ducted to it.
93. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the total combined VOC emissions from the ethanol loadout operation shall not exceed 0.27 pound per hour and 1.17 tons in any 12-consecutive month period.
94. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the total combined volatile HAP emissions from the ethanol loadout operation shall not exceed 0.0050 pound per hour and 0.022 ton in any 12-consecutive month period.
95. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the total combined CO emissions from the ethanol loadout operation shall not exceed 0.42 pound per hour and 1.82 tons in any 12-consecutive month period.
96. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the total combined NOx emissions from the ethanol loadout operation shall not exceed 0.19 pound per hour and 0.78 ton in any 12-consecutive month period.
97. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the total combined PM emissions from the ethanol loadout operation shall not exceed 0.00013 grain per dry standard cubic foot of effluent gas volume, 0.0032 pound per hour and 0.014 ton in any 12-consecutive month period.
98. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the total combined PM10 emissions from the ethanol loadout operation shall not exceed 0.00013 grain per dry standard cubic foot of effluent gas volume, 0.0032 pound per hour and 0.014 ton in any 12-consecutive month period.
99. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, all VOC and/or volatile HAP-containing vapors displaced from railcars and trucks being loaded with ethanol shall be collected through dedicated vapor collection lines and ducted to the enclosed flare for destruction. Flexible boots on truck or railcar hatches shall not be used for vapor collection.
100. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the enclosed flare shall be equipped with an auxiliary fuel system (natural gas) and shall achieve a combustion chamber temperature of 1,600° F prior to the commencement of each occasion of ethanol loadout.
101. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the enclosed flare shall be equipped with a continuous temperature monitoring and recording system and an interlock system that will automatically shut down loading operations if the flare's combustion chamber temperature falls below 1,600° F.
102. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall develop and submit to the Department for approval a quality control program for the combustion chamber temperature monitor associated with the enclosed flare. The quality control program shall include, at a minimum, a written protocol that describes the calibration and maintenance procedures and schedules to be used for the monitor to ensure its integrity and accuracy. In addition, the quality control program shall identify the calibration and maintenance records which will be maintained. The permittee shall keep the quality control program on file for the life of the enclosed flare and all associated calibration and maintenance records for a minimum of 5 years. The quality control program, including associated calibration and maintenance records, shall be made available to the Department upon request.
103. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, no more than 92.63 million gallons of denatured ethanol shall be loaded out in any 12-consecutive month period. Records shall be maintained of the amount of denatured ethanol loaded out during each month. All records generated under this condition shall be retained for at least 5 years and shall be made available to the Department upon request.
104. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall submit semi-annual reports to the Department listing the amount of denatured ethanol loaded out during each month of the respective reporting period. Each semi-annual report shall be submitted to the Department by no later than September 1 (for the immediately-preceding January 1 through June 30 period) and March 1 (for the immediately-preceding July 1 through December 31 period).
105. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, within 90 days of commencing operation of the second ethanol loadout rack, but no later than 180 days of commencing operation of the first ethanol loadout rack, the permittee shall perform stack testing on the enclosed flare to determine its VOC and NOx emission rates. All testing is to be performed using test methods and procedures which are acceptable to the Department while both loadout racks are in use.
106. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the VOC and NOx source testing required by condition in paragraph (105) herein shall be repeated once every 2 years after initial testing occurs.
107. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the total combined VOC emissions from the two ethanol day tanks, the denaturant storage tank, the two denatured ethanol storage tanks and the No. 2 fuel oil storage tank shall not exceed 1.11 tons in any 12-consecutive month period.
108. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the total combined volatile HAP emissions from the two ethanol day tanks, the denaturant storage tank, the two denatured ethanol storage tanks and the No. 2 fuel oil storage tank shall not exceed 0.045 ton in any 12-consecutive month period.
109. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12 as well as 40 CFR 60.112b, the denaturant storage tank and the two denatured ethanol storage tanks shall have internal floating roofs which incorporate a vapor-mounted primary seal and a rim-mounted secondary seal.
110. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the two ethanol day tanks shall have internal floating roofs which incorporate a vapor-mounted primary seal and a rim-mounted secondary seal.
111. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12 as well as 40 CFR 60.112b, all openings (except stub drains) in the internal floating roofs of the denaturant storage tank and the two denatured ethanol storage tanks shall be equipped with covers, lids or seals such that: each cover, lid or seal will be in the closed position at all times except when in actual use, automatic bleeder vents will be closed at all times except when the roof is floated off or landed on the roof leg supports and that rim vents, if provided, will be set to open when the roof is being floated.
112. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, all openings (except stub drains) in the internal floating roofs of the two ethanol day tanks shall be equipped with covers, lids or seals such that: each cover, lid or seal will be in the closed position at all times except when in actual use, automatic bleeder vents will be closed at all times except when the roof is floated off or landed on the roof leg supports and that rim vents, if provided, will be set to open when the roof is being floated.
113. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12 as well as 40 CFR 60.112b, best management practices shall be used to minimize the occurrence of internal floating roof landing episodes in the denaturant storage tank and the two denatured ethanol storage tanks.
114. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, best management practices shall be used to minimize the occurrence of internal floating roof landing episodes in the two ethanol day tanks.
115. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12 as well as 40 CFRs 60.113b and 60.115b, annual inspections of the internal floating roofs of the denaturant storage tank and the two denatured ethanol storage tanks shall be conducted and the results recorded. All records generated under this condition shall be retained for at least 5 years and shall be made available to the Department upon request.
116. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, annual inspections of the internal floating roofs of the two ethanol day tanks shall be conducted and the results recorded. All records generated under this condition shall be retained for at least 5 years and shall be made available to the Department upon request.
117. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the shells and roofs of the two ethanol day tanks, the denaturant storage tank, the two denatured ethanol storage tanks and the No. 2 fuel oil storage tank shall be white.
118. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the combined throughput of the two ethanol day tanks shall not exceed 88 million gallons in any 12-consecutive month period, the throughput of the denaturant storage tank shall not exceed 4.63 million gallons in any 12-consecutive month period, the combined throughput of the two denatured ethanol storage tanks shall not exceed 92.63 million gallons in any 12-consecutive month period and the throughput of the No. 2 fuel oil storage tank shall not exceed 282,900 gallons in any 12-consecutive month period.
119. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall maintain records of the type of volatile liquid stored in each tank during each month, the throughput of each tank during each month and the maximum true vapor pressure of the volatile liquid stored in each tank during each month. All records generated under this condition shall be maintained for at least 5 years and shall be made available to the Department upon request.
120. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall submit an annual report to the Department listing the type of volatile liquid stored in each tank during each month of the prior year, the throughput of each tank during each month of the prior year and the maximum true vapor pressure of the volatile liquid stored in each tank during each month of the prior year. Each annual report shall be submitted to the Department by no later than March 1 (for the immediately-preceding January 1 through December 31 period).
121. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall maintain records of the amount of VOCs and volatile HAPs emitted from each tank during each month other than those emissions resulting from internal floating roof landings as well as the amount of VOCs and volatile HAPs emitted from each tank during each month as a result of internal floating roof landings, when applicable. These records shall include a copy of all calculations performed in determining these emission values and a description of all assumptions made in performing the calculations. All records generated under this condition shall be maintained for at least 5 years and shall be made available to the Department upon request.
122. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall submit an annual report to the Department listing the amount of VOCs and volatile HAPs emitted from each tank during each month of the prior year other than those emissions resulting from internal floating roof landings as well as the amount of VOCs and volatile HAPs emitted from each tank during each month of the prior year as a result of internal floating roof landings, when applicable. These reports shall include a copy of all calculations performed in determining these emission values and a description of all assumptions made in performing the calculations. Each annual report shall be submitted to the Department by no later than March 1 (for the immediately-preceding January 1 through December 31 period).
123. The two ethanol day tanks, the denaturant storage tank and the two denatured ethanol storage tanks shall comply will all applicable requirements specified in 25 Pa. Code § 129.56.
124. The denaturant storage tank and the two denatured ethanol storage tanks are subject to Subpart Kb of the Federal Standards of Performance for New Stationary Sources, 40 CFR 60.110b--60.117b (Standards of Performance for VOC Liquid Storage Vessels). The permittee shall comply with all applicable requirements of this Subpart as well as any other applicable Subparts of the Standards of Performance, including all recordkeeping and reporting requirements. Under 40 CFR 60.4 of the Standards of Performance, the submission of all requests, reports, applications, submittals and other communications required by the Standards of Performance must be made to both the Department of Environmental Protection and the Environmental Protection Agency. The Environmental Protection Agency copies may be sent to:
U. S. EPA Region III
Air Protection Division
Office of Enforcement and Permits (3AP10)
1650 Arch Street
Philadelphia, PA 19103
and
The Pennsylvania Department of Environmental
Protection
Air Quality Program Manager
208 W. Third Street, Suite 101
Williamsport, PA 17701-6448125. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the total combined fugitive VOC emissions resulting from equipment leaks shall not exceed 1.92 pounds per hour or 8.41 tons in any 12-consecutive month period.
126. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall implement a leak detection and repair program (LDAR) which is compliant with Subpart VV of the Federal Standards of Performance for New Stationary Sources, 40 CFR 60.480--60.489 (Standards of Performance for Equipment Leaks of VOC in the Synthetic Organic Chemicals Manufacturing Industry).
127. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall maintain records of the amount of fugitive VOCs emitted from equipment leaks during each month. These records shall include a copy of all calculations performed in determining these emission values and a description of all assumptions made in performing the calculations. All records generated under this condition shall be maintained for at least 5 years and shall be made available to the Department upon request.
128. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall submit an annual report to the Department listing the amount of fugitive VOCs emitted from equipment leaks during each month of the prior year. These reports shall include a copy of all calculations performed in determining these emission values and a description of all assumptions made in performing the calculations. Each annual report shall be submitted to the Department by no later than March 1 (for the immediately-preceding January 1 through December 31 period).
129. This facility is subject to Subpart VV of the Federal Standards of Performance for New Stationary Sources, 40 CFR 60.480 through 60.489 (Standards of Performance for Equipment Leaks of VOC in the Synthetic Organic Chemicals Manufacturing Industry). The permittee shall comply with all applicable requirements of this Subpart as well as any other applicable Subparts of the Standards of Performance, including all recordkeeping and reporting requirements. Under 40 CFR 60.4 of the Standards of Performance, the submission of all requests, reports, applications, submittals and other communications required by the Standards of Performance must be made to both the Department of Environmental Protection and the Environmental Protection Agency. The Environmental Protection Agency copies may be sent to:
U. S. EPA Region III
Air Protection Division
Office of Enforcement and Permits (3AP10)
1650 Arch Street
Philadelphia, PA 19103
and
The Pennsylvania Department of Environmental
Protection
Air Quality Program Manager
208 W. Third Street, Suite 101
Williamsport, PA 17701-6448130. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of SOx, expressed as SO2, from the CFB boiler shall not exceed 0.31 pound per million Btu of heat input based on a 3-hour rolling average basis, 0.278 pound per million Btu of heat input based on a 24-hour rolling average basis, 0.20 pound per million Btu of heat input based on a 30-day rolling average basis and 435.2 tons in any 12-consecutive month period.
131. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of NOx, expressed as NO2, from the CFB boiler shall not exceed 0.10 pound per million Btu of heat input on a 24-hour rolling average basis, 0.07 pound per million Btu of heat input on a 30-day rolling average basis and 152.32 tons in any 12-consecutive month period.
132. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of CO from the CFB boiler shall not exceed 0.15 pound per million Btu of heat input, 74.52 pounds per hour and 326.4 tons in any 12-consecutive month period.
133. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of sulfuric acid mist from the CFB boiler shall not exceed 0.01 pound per million Btu of heat input, 4.97 pounds per hour and 21.76 tons in any 12-consecutive month period.
134. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of filterable 10, from the CFB boiler shall not exceed 0.01 pound per million Btu of heat input, 4.97 pounds per hour and 21.76 tons in any 12-consecutive month period. Additionally, the emission of total filterable PM, including filterable PM10, shall not exceed 0.01 pound per million Btu of heat input, 4.97 pounds per hour and 21.76 tons in any 12-consecutive month period.
135. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of total PM10 (filterable and condensable) from the CFB boiler shall not exceed 0.05 pound per million Btu of heat input, 24.84 pounds per hour and 108.8 tons in any 12-consecutive month period.
136. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the visible air contaminant emissions from the CFB boiler shall not have an opacity in excess of 10% at any time.
137. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of VOCs from the CFB boiler shall not exceed 0.005 pound per million Btu of heat input, 2.49 pounds per hour and 10.88 tons in any 12-consecutive month period.
138. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of ammonia from the CFB boiler shall not exceed 10 parts per million by volume dry basis corrected to 7% oxygen, 0.0065 pound per million Btu of heat input, 3.23 pounds per hour and 14.15 tons in any 12-consecutive month period.
139. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of mercury from the CFB boiler shall not exceed 0.0096 pound per gigawatt-hour (GWh) or the rate reflecting at least 95% control of the total mercury input into the boiler in the waste coal and shall also not exceed 2.1 pounds in any 12-consecutive month period.
140. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of lead from the CFB boiler shall not exceed 28.4 pounds per trillion Btu of heat input, 0.014 pound per hour and 123.6 pounds in any 12-consecutive month period.
141. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of beryllium from the CFB boiler shall not exceed 8.58 pounds per trillion Btu of heat input, 0.0043 pound per hour and 37.34 pounds in any 12-consecutive month period.
142. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of hydrogen chloride from the CFB boiler shall not exceed 0.00457 pound per million Btu of heat input, 2.27 pounds per hour and 9.94 tons in any 12-consecutive month period.
143. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of hydrogen fluoride from the CFB boiler shall not exceed 0.0014 pound per million Btu of heat input, 0.7 pound per hour and 3.05 tons in any 12-consecutive month period.
144. The Department reserves the right to establish additional HAP emission limitations for the CFB boiler after the determination of emission rates by stack testing.
145. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, only waste bituminous coal shall be fired in the CFB boiler and the sulfur content of the waste coal, as blended for use in the boiler, shall not exceed 4% by weight at any time. Additionally, the permittee shall not burn residual, municipal, hazardous, hospital, infectious or chemotherapeutic wastes or any other material not specifically approved in this plan approval.
146. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the CFB boiler shall not burn more 302,220 tons of waste bituminous coal in any 12-consecutive month period.
147. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the CFB boiler shall have a maximum heat input rate of 496.8 million Btu per hour and the associated air contaminants shall be controlled by a limestone injection system, a selective noncatalytic reduction system, a flash dryer absorber or spray dryer absorber system, a cyclone and a fabric collector.
148. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the CFB boiler shall not operate without the simultaneous operation of the associated limestone injection system, selective noncatalytic reduction system, flash dryer absorber or spray dryer absorber system, cyclone and fabric collector.
149. Within 30 days of selection of the specific CFB boiler, selective noncatalytic reduction system, flash dryer absorber or spray dryer absorber system, cyclone and fabric collector the permittee proposes to install, the permittee shall notify the Department of the manufacturer and model of the respective piece of equipment selected and shall additionally, at the same time, submit to the Department for review specifications for the respective piece of equipment that are comprehensive enough to allow the Department to determine if the selected piece of equipment is equivalent to that proposed in the plan approval application.
150. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the fabric collector controlling the CFB boiler shall have an effective air to cloth ratio at actual conditions of no more than 5:1 and the collector bags shall be cleaned using reverse air jets.
151. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the selective noncatalytic reduction system associated with the CFB boiler shall be installed upstream of the cyclone.
152. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the selective noncatalytic reduction system associated with the CFB boiler shall be equipped with instrumentation to continuously monitor the actual flow rate and totalized flow of the reagent, the pressure of the reagent, the reagent pump for verification of operation and the temperature of the reagent at or close to the delivery point. Each continuously-monitored parameter shall be recorded and alarms shall be incorporated into the monitoring systems to notify the operators of any conditions outside the normal operating range.
153. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the CFB boiler fabric collector shall be insulated and shall have heaters and a temperature control system to protect the fabric collector and filter bags. Additionally, the dust hoppers of the fabric collector shall be insulated and shall have level detectors and vibrators.
154. The CFB boiler shall exhaust to the atmosphere at a height of no less than 315.55 feet above grade. Additionally, the inside diameter of the flue shall be no greater than 8.5 feet at the point of exhaust.
155. Within 60 days of achieving maximum production, but no later than 180 days after initial startup, the permittee shall perform stack testing on the CFB boiler to determine the SOx, NOx, VOC, CO, filterable PM10, total filterable particulate including filterable PM10, total PM10 (filterable and condensable), sulfuric acid mist, ammonia, hydrogen fluoride, hydrogen chloride, mercury, beryllium and lead emission rates. Representative as-fired coal samples shall be taken at the time of the mercury and hydrogen chloride stack testing to accurately determine the mercury and chlorine content of the waste coal fired during this testing. In addition, antimony, arsenic, cadmium, chromium, cobalt, manganese, nickel and selenium stack tests shall be performed to determine the emission rates of these HAPs. Representative as-fired coal samples shall also be taken during these stack tests to accurately determine the antimony, arsenic, cadmium, chromium, cobalt, manganese, nickel and selenium content of the waste coal fired during the testing. Sunnyside shall also submit a test plan with the stack test protocol for the testing of organic HAPs. The NOx and CO stack testing shall be conducted simultaneously. All testing shall be performed while the CFB boiler is operating at maximum capacity using test methods and procedures approved by the Department. These tests shall be repeated on a yearly basis. The permittee may request a change in the frequency of the testing once enough data has been generated to determine the consistency of the results.
156. At least 180 days prior to the anticipated startup of the CFB boiler, the permittee shall submit to the Department a waste coal sampling plan which shall include the proposed frequency of sampling (daily, weekly, etc.), the proposed frequency of sample analysis (daily, weekly, and the like), the proposed sample locations, the specific procedures to be used for collecting and preparing the samples and the fuel characteristics for which each sample will be analyzed (sulfur content, ash content, heat of combustion, chlorine content, and the like). This sampling plan shall also specifically address the sampling and sample analysis frequency for mercury and chlorine.
157. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall install, certify, maintain and operate continuous emission monitoring systems (CEMSs) for NOx, CO and SOx as well as oxygen (or CO2) and opacity on the CFB boiler in accordance with all applicable requirements specified in 25 Pa. Code Chapter 139 and the Department's Continuous Source Monitoring Manual. All of the CEMSs specified above shall be installed prior to startup of the respective CFB boiler. No CEMS may however be installed unless Phase I approval has first been obtained from the Department. The NOx, CO, SOx, opacity and oxygen (or CO2) emission monitoring systems shall be capable of monitoring compliance with all applicable emission limits specified for the respective air contaminants herein.
158. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall submit a Phase I application to the Department for the NOx, CO, SOx, oxygen (or CO2) and opacity continuous emission monitoring systems at least 6 months prior to the anticipated startup date of the CFB boiler.
159. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the CFB boiler shall not be operated for any reason unless the associated NOx, CO, SOx, oxygen (or CO2) and opacity continuous emission monitoring systems have received Phase I approval from the Department and have subsequently been installed and made operational in accordance with the conditions of this plan approval. Furthermore, the continuous emission monitoring systems shall be operated any time the CFB boiler is operating in accordance with all applicable requirements specified in 25 Pa. Code Chapter 139, as well as with the Department's Continuous Source Monitoring Manual, unless superseded by conditions contained in this plan approval. The required relative accuracy testing shall have been completed on the associated continuous emission monitoring systems and the monitoring systems shall be fully certified in accordance with the Department's Continuous Source Monitoring Manual within 180 days of startup of the CFB boiler.
160. The permittee shall submit all reports to the Department associated with the continuous emission monitoring systems for NOx, CO, SOx, oxygen (or CO2) and opacity in accordance with all applicable requirements specified in 25 Pa. Code Chapter 139 and the Department's Continuous Source Monitoring Manual.
161. The permittee shall maintain comprehensive accurate records for the CFB boiler which shall be adequate to allow compliance to be determined with the requirements contained in all conditions contained herein. At a minimum, these records shall include:
a. The total tons of waste bituminous coal that are burned in the CFB boiler each month.
b. The results from the waste coal sulfur content analyses.
c. The results from the as-fired waste coal mercury and chlorine content analyses.
d. The gross megawatt per hour output of the generator associated with the CFB (on a continuous basis).
e. The differential pressure across the fabric collector and the inlet temperature (on a continuous basis).
f. The calculated ammonia emission rate, all associated calculations and all supporting data (to be used to verify compliance with the ammonia emission limitations contained herein).
g. The calculated mercury emission rate, all associated calculations and all supporting data (to be used to verify compliance with mercury emission limitations contained herein).
h. The calculated lead emission rate, all associated calculations and all supporting data (to be used to verify compliance with the lead emission limitations contained herein).
i. The calculated beryllium emission rate, all associated calculations and all supporting data (to be used to verify compliance with the beryllium emissions limitations contained herein).
j. The calculated hydrogen chloride emission rate, all associated calculations and all supporting data (to be used to verify compliance with the hydrogen chloride emission limitations contained herein).
k. The calculated hydrogen fluoride emission rate all associated calculations and all supporting data to be used to verify compliance with the hydrogen fluoride emission limitations contained herein.
All records generated under this condition shall be retained for at least 5 years and shall be made available to the Department upon request.
162. The permittee shall provide quarterly compliance demonstration reports for the mercury and hydrogen chloride emissions from the CFB boiler. Each compliance demonstration report shall include the calculated mercury and hydrogen chloride emission rates which occurred during the respective calendar quarter, all associated calculations and all supporting data, including the results of all waste coal mercury and chlorine analyses performed during the respective calendar quarter. Each quarterly compliance demonstration report shall be submitted to the Department by no later than June 1 of each year (containing the records generated for the immediately-preceding January 1 through March 31 3-month period), September 1 of each year (containing the records generated for the immediately-preceding April 1 through June 30 3-month period), December 1 of each year (containing the records generated for the immediately-preceding July 1 through September 30 3-month period) and March 1 of each year (containing the records generated for the immediately-preceding October 1 through December 31 3-month period).
163. The permittee shall submit reports to the Department on a semi-annual basis that include:
a. The amount of waste bituminous coal used in the prior 6 consecutive month period.
b. The calculated ammonia, lead, beryllium and hydrogen fluoride emission rates which occurred during the prior 6 consecutive month period, all associated calculations and all supporting data.
The semi-annual reports shall be submitted to the Department by no later than September 1 of each year (containing the records generated for the immediately-preceding January through June 6-month period) and March 1 of each year (containing the records generated for the immediately-preceding July through December 6-month period).
164. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the permittee shall develop and submit to the Department for approval a quality control program for the continuous differential pressure drop monitor and inlet temperature monitor for the CFB boiler fabric collector as well as the continuous reagent flow rate monitor, totalized reagent flow rate monitor, reagent pressure monitor, the reagent pump operation verification monitor and reagent delivery point temperature monitor for the selective noncatalytic reduction system and any other continuous monitor used for monitoring operating parameters for the CFB boiler or associated control devices. The quality control program shall include, at a minimum, a written protocol that describes the calibration and maintenance procedures and schedules to be used for each monitor to ensure its integrity and accuracy. In addition, the quality control program shall identify the calibration and maintenance records which will be maintained. The permittee shall keep the quality control program on file for the life of the CFB boiler and all associated calibration and maintenance records for a minimum of 5 years. The quality control program, including associated calibration and maintenance records, shall be made available to the Department upon request.
165. The CFB boiler is subject to Subpart Db of the Federal New Source Performance Standards, 40 CFR 60.40b--60.49b. The permittee shall comply with all applicable requirements of this Subpart as well as any other applicable Subpart of the Standards of Performance, including all recordkeeping and reporting requirements. Under 40 CFR 60.4 of the Standards of Performance, the submission of all requests, reports, applications, submittals and other communications required by the Standards of Performance must be made to both the Department of Environmental Protection and the Environmental Protection Agency. The Environmental Protection Agency copies may be sent to:
U. S. EPA Region III
Air Protection Division
Office of Enforcement and Permits (3AP10)
1650 Arch Street
Philadelphia, PA 19103
and
The Pennsylvania Department of Environmental
Protection
Air Quality Program Manager
208 W. Third Street, Suite 101
Williamsport, PA 17701-6448166. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the auxiliary boiler shall have a maximum heat input rate of 76 million Btu per hour, shall incorporate the use of a low NOx burner and flue gas recirculation and shall only fire virgin No. 2 fuel oil or natural gas.
167. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the auxiliary boiler shall be operated for no more than 1,000 hours in any 12-consecutive month period of which no more than 100 hours may be while the boiler is being fired on virgin No. 2 fuel oil.
168. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the auxiliary boiler shall be equipped with instrumentation to monitor and record the usage of natural gas and No. 2 fuel oil.
169. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of SOx, expressed as SO2, from the auxiliary boiler shall not exceed 0.0006 pound per million Btu of heat input and 0.046 pound per hour while firing natural gas, 0.052 pound per million Btu of heat input and 3.96 pounds per hour while firing No. 2 fuel oil and 0.22 ton in any 12-consecutive month period.
170. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of NOx, expressed as NO2, from the auxiliary boiler shall not exceed 0.035 pound per million Btu of heat input and 2.66 pounds per hour when firing natural gas, 0.072 pound per million Btu of heat input and 5.48 pounds per hour when firing No. 2 fuel oil and 1.471 tons in any 12-consecutive month period.
171. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of CO from the auxiliary boiler shall not exceed 0.037 pound per million Btu of heat input and 2.82 pounds per hour while firing natural gas, 0.036 pound per million Btu of heat input and 2.74 pounds per hour while firing No. 2 fuel oil and 1.41 tons in any 12-consecutive month period.
172. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of PM from the auxiliary boiler shall not exceed 0.024 pound per million Btu of heat input and 1.83 pounds per hour while firing No. 2 fuel oil and 0.0075 pound per million Btu of heat input and 0.57 pound per hour while firing natural gas. The emission of PM10 from the auxiliary boiler shall not exceed 0.017 pound per million Btu of heat input and 1.30 pounds per hour while firing No. 2 fuel oil and 0.0075 pound per million Btu of heat input and 0.57 pound per hour while firing natural gas. Additionally, the PM emissions shall not exceed 0.35 ton in any 12-consecutive month period and the PM10 emissions shall not exceed 0.321 ton in any 12-consecutive month period.
173. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and of 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the visible air contaminant emissions from the auxiliary boiler shall not have an opacity in excess of 10% at any time.
174. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of VOCs from the auxiliary boiler shall not exceed 0.0054 pound per million Btu of heat input and 0.41 pound per hour while firing natural gas, 0.0014 pound per million Btu of heat input and 0.11 pound per hour while firing No. 2 fuel oil and 0.21 ton in any 12-consecutive month period.
175. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of HAPs from the auxiliary boiler shall not exceed 142 pounds in any 12-consecutive month period.
176. The permittee shall maintain comprehensive accurate records for the auxiliary boiler which shall be adequate to allow compliance to be determined with the requirements contained in all conditions contained herein. At a minimum, these records shall include the amount of each type of fuel used in the auxiliary boiler each month. All records generated under this condition shall be retained for at least 5 years and shall be made available to the Department upon request.
177. The permittee shall submit reports to the Department on a semi-annual basis of the amount of each type of fuel used in the auxiliary boiler during the prior 6-consecutive month period. The semi-annual reports shall be submitted to the Department by no later than September 1 of each year (containing the records generated for the immediately-preceding January through June 6-month period) and March 1 of each year (containing the records generated for the immediately-preceding July through December 6-month period).
178. The auxiliary boiler is subject to Subpart Dc of the Federal New Source Performance Standards, 40 CFR 60.40c--60.48c. The permittee shall comply with all applicable requirements of this Subpart as well as any other applicable Subpart of the Standards of Performance, including all recordkeeping and reporting requirements. Under 40 CFR 60.4 of the Standards of Performance, the submission of all requests, reports, applications, submittals and other communications required by the Standards of Performance must be made to both the Department of Environmental Protection and the Environmental Protection Agency. The Environmental Protection Agency copies may be sent to:
U. S. EPA Region III
Air Protection Division
Office of Enforcement and Permits (3AP10)
1650 Arch Street
Philadelphia, PA 19103
and
The Pennsylvania Department of Environmental
Protection
Air Quality Program Manager
208 W. Third Street, Suite 101
Williamsport, PA 17701-6448179. Within 30 days of selection of the specific auxiliary boiler the permittee proposes to install, the permittee shall notify the Department of the manufacturer and model of the specific boiler selected and shall additionally, at the same time, submit to the Department for review specifications for the boiler that are comprehensive enough to allow the Department to determine if the selected boiler is equivalent to that proposed in the plan approval application.
180. Within 60 days of achieving maximum production, but no later than 180 days after initial startup, the permittee shall perform stack testing on the auxiliary boiler while firing natural gas to determine the NOx and CO emission rates. Additionally, a Method 9 opacity test shall be performed on the boiler. The NOx and CO stack testing shall be conducted simultaneously. All testing shall be performed while the auxiliary boiler is operating at maximum capacity, using test methods and procedures approved by the Department. The CO and NOx tests shall be repeated every 3 years. The permittee may request a change in the frequency of the testing once enough data has been generated to determine the consistency of the results.
181. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the three emergency generators shall each be a Caterpillar Model: 3516CTA, or equivalent (as determined by the Department), shall each be rated at no more than 2,681 horsepower, shall incorporate the use of ignition timing retard and shall only fire virgin diesel fuel or No. 2 fuel oil.
182. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, each emergency generator shall be operated for no more than 300 hours in any 12-consecutive month period.
183. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, each emergency generator shall be equipped with a nonresettable hour meter.
184. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of SOx, expressed as SO2, from each emergency generator shall not exceed 0.166 gram per brake horsepower-hour and 0.15 ton in any 12-consecutive month period.
185. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of NOx, expressed as NO2, from each emergency generator shall not exceed 5.39 grams per brake horsepower-hour and 4.78 tons in any 12-consecutive month period.
186. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of CO from each emergency generator shall not exceed 0.29 grams per brake horsepower-hour and 0.26 tons in any 12-consecutive month period.
187. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of PM from each emergency generator shall not exceed 0.026 gram per brake horsepower-hour and 0.023 ton in any 12-consecutive month period.
188. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of PM10 from each emergency generator shall not exceed 0.026 gram per brake horsepower-hour and 0.023 ton in any 12-consecutive month period.
189. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of nonmethane hydrocarbons from each emergency generator shall not exceed 0.11 gram per brake horsepower-hour and 0.1 ton in any 12-consecutive month period.
190. Under the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the emission of HAPs from each emergency generator shall not exceed 0.003 ton in any 12-consecutive month period.
191. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the visible air contaminant emissions from each emergency generator shall not equal or exceed 10% opacity for a period or periods aggregating more than 3 minutes in any one hour or equal or exceed 30% opacity at any time.
192. Within 180 days of the commencement of operation of each emergency generator, stack testing shall be performed on the respective generator to determine its NOx, nonmethane hydrocarbon and CO emission rates using reference method test procedures which are acceptable to the Department. In addition to the stack testing required by this condition, within 12 months after the initial stack testing and annually thereafter, the permittee shall perform NOx and CO emission tests upon each emergency generator using a portable analyzer approved by the Department. The Department may alter the frequency of annual portable analyzer tests once enough data has been generated to determine the consistency of the results.
193. The permittee shall maintain comprehensive accurate records for the emergency generators which shall be adequate to allow compliance to be determined with the requirements contained in all conditions contained herein. At a minimum, these records shall include:
a. The type and amount (gallons) of fuel used in the emergency generators each month.
b. The number of hours that each emergency generator operates each month.
All records generated under this condition shall be retained for at least 5 years and shall be made available to the Department upon request.
194. The permittee shall submit reports to the Department on a semi-annual basis that include:
a. The type and amount (gallons) of fuel used in the emergency generators during the prior 6-consecutive month period.
b. The number of hours that each emergency generator operates each month during the prior 6-consecutive month period.
The semi-annual reports shall be submitted to the Department by no later than September 1 of each year (containing the records generated for the immediately-preceding January through June 6-month period) and March 1 of each year (containing the records generated for the immediately-preceding July through December 6-month period).
195. The three emergency generators are subject to Subpart IIII of the Federal New Source Performance Standards, 40 CFR 60.4200--60.4219. The permittee shall comply with all applicable requirements of this Subpart as well as any other applicable Subpart of the Standards of Performance, including all recordkeeping and reporting requirements. Under 40 CFR 60.4 of the Standards of Performance, the submission of all requests, reports, applications, submittals and other communications required by the Standards of Performance must be made to both the Department of Environmental Protection and the Environmental Protection Agency. The Environmental Protection Agency copies may be sent to:
U. S. EPA Region III
Air Protection Division
Office of Enforcement and Permits (3AP10)
1650 Arch Street
Philadelphia, PA 19103
and
The Pennsylvania Department of Environmental
Protection
Air Quality Program Manager
208 W. Third Street, Suite 101
Williamsport, PA 17701-6448196. Within 30 days of selection of the specific emergency generators the permittee proposes to install, the permittee shall notify the Department of the manufacturer and model of the emergency generators selected and shall additionally, at the same time, submit to the Department for review specifications for the emergency generators that are comprehensive enough to allow the Department to determine if the selected emergency generators are equivalent to those proposed in the plan approval application.
197. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, the two fire pump engines shall each be a Clarke Fire Products, Inc. Model: JW6H-UF60, or equivalent (as determined by the Department of Environmental Protection), shall each be rated at no more than 360 horsepower, shall incorporate the use of ignition timing retard, lean burn technology and shall only fire virgin diesel fuel or No. 2 fuel oil.
198. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, each fire pump engine shall be operated for no more than 500 hours in any 12-consecutive month period.
199. Under the Prevention of Significant Deterioration provisions of 40 CFR 52.21 and 25 Pa. Code § 127.83, as well as the New Source Review provisions of 25 Pa. Code §§ 127.201--127.217 and the BAT provision of 25 Pa. Code §§ 127.1 and 127.12, each fire pump engine shall be equipped with a nonresettable hour meter.
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