Permit #	Permit Description
B000001	ATC	Basic	COAL UNLOADING SYSTEM
B000080	PTO	Basic	CRUSHER - PRIMARY LIMESTONE
B000081	PTO	Basic	CRUSHER - SECONDARY LIMESTONE
B000082	PTO	Basic	LIMESTONE SHIPPING
B000083	ATC	Basic	RAW MATERIAL SYSTEM - NO. 1
B000085	PTO	Basic	CLINKER LOADOUT SYSTEM - RAIL
B001083	PTO	Basic	KILN (Q2) AND CLINKER COOLER SYSTEM
B001084	PTO	Basic	RAW MILL NO. 2 SYSTEM
B001085	PTO	Basic	COAL/COKE TRANSFER EQUIPMENT
B001264	PTO	Basic	COAL UNLOADING SYSTEM
B001289	PTO	Basic	LIMESTONE RECLAIM SYSTEM
B001666	ATC	Basic	LIMESTONE STACKING SYSTEM - STORAGE
B001672	PTO	Basic	CLINKER TRANSFER SYSTEM TO OUTSIDE STORAGE
B001673	PTO	Basic	CLINKER TRANSFER SYSTEM - STORAGE SILO NO. 1
B001674	PTO	Basic	CLINKER TRANSFER SYSTEM - STORAGE SILO NO. 2
B001675	PTO	Basic	CLINKER TRANSFER SYSTEM - STORAGE DOME
B001676	PTO	Basic	CLINKER RECLAIM SYSTEM - OUTSIDE STORAGE
B001677	PTO	Basic	CLINKER RECLAIM SYSTEM - STORAGE DOME
B001678	PTO	Basic	CLINKER RECLAIM SYSTEM - STORAGE SILO NO. 1
B001679	PTO	Basic	CLINKER RECLAIM SYSTEM - STORAGE SILO NO. 2
B002709	PTO	Basic	BULK TRUCK & SUPER SACK LOADOUT FACILITY
B005344	PTO	Basic	COAL STACKER & RECLAIM SYSTEM
B005362	ATC	Basic	KILN (Q3) AND CLINKER COOLER SYSTEM
B007336	ATC	Basic	ROLL PRESS No. 1, RAW MATERIAL GRINDING
B007340	ATC	Basic	KILN Q3 PRE-HEATER FEED SYSTEM
B007364	ATC	Basic	ROLL PRESS No. 2, RAW MATERIAL GRINDING
B007709	PTO	Basic	CLINKER OUTSIDE STORAGE RECLAIM SYSTEM
C000087	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (DBH3)
C000092	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (HBH 6)
C000093	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (HBH 17)
C000095	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (EBH1)
C001090	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (GBH2)
C001091	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (GGF 2)
C001290	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (CBH1)
C001291	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (CBH2)
C001292	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (DBH5)
C001293	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (DBH2)
C001294	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (EBH3)
C001295	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (EBH4)
C001296	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (DBH4)
C001297	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (HBH 1)
C001298	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (HBH 2)
C001299	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (EBH 5)
C001300	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (HBH 19)
C001301	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (HBH 3)
C001302	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (HBH 4)
C001303	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT
C001308	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (HBH 18)
C001660	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (HBH 20)
C001667	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (DBH1)
C001668	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (EBH2)
C001669	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (HBH 22)
C001670	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (HBH 21)
C002081	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT
C002082	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT
C002710	PTO	Air Pollution Control Device	AIR POLLUTION CONTROL EQUIPMENT (GWDBH)
C003249	PTO	Air Pollution Control Device	BAGHOUSE (QBH1)
C004870	PTO	Air Pollution Control Device	BAGHOUSE (HBH24)
C004871	PTO	Air Pollution Control Device	BAGHOUSE (HBH23)
C005190	PTO	Air Pollution Control Device	K2 G-COOLER DUST COLLECTOR (GGC BH)
C007337	PTO	Air Pollution Control Device	BAGHOUSE, CBH3, at Drop Tube from CBC8 (B001666), RAW MATERIAL TRANSPORT SYSTEM
C007347	PTO	Air Pollution Control Device	BAGHOUSE- HBH25, WHICH SERVES THE KILN Q-3 CLINKER PAN CONVEYOR
C007348	PTO	Air Pollution Control Device	BAGHOUSE- EBH6, WHICH SERVES THE KILN Q-3 PRE-HEATER SYSTEM
C007350	PTO	Air Pollution Control Device	BAGHOUSE- EBH7, CONTROL DEVICE FOR KILN Q-3 PRE-HEATER FEED SYSTEM
C007351	PTO	Air Pollution Control Device	BAGHOUSE- EBH8, WHICH SERVES KILN Q-3 PRE-HEATER FEED SYSTEM
C007353	PTO	Air Pollution Control Device	BAGHOUSE- DBH13, WHICH SERVES RAW MATERIAL TRANSPORT SYSTEM
C007355	PTO	Air Pollution Control Device	BAGHOUSE-DBH14, CONTROLLING EMISSIONS FROM THE RAW MATERIAL TRANSPORT SYSTEM
C007356	PTO	Air Pollution Control Device	BAGHOUSE-DBH15
C007358	ATC	Air Pollution Control Device	BAGHOUSE- (FPFB4DC), WHICH SERVES THE NEW PULVERIZED COAL BIN
C007359	ATC	Air Pollution Control Device	BAGHOUSE-FBH4P1
C007360	ATC	Air Pollution Control Device	BAGHOUSE- DBH 9, WHICH SERVES ROLL PRESS 1(MATERIAL GRINDING)
C007361	ATC	Air Pollution Control Device	BAGHOUSE DBH 7, WHICH SERVES ROLL PRESS No. 1
C007362	ATC	Air Pollution Control Device	BAGHOUSE-DBH 8, WHICH SERVES ROLL PRESS No.1
C007363	ATC	Air Pollution Control Device	BAGHOUSE- DBH 13, WHICH SERVES ROLL PRESS No.1
C007365	ATC	Air Pollution Control Device	BAGHOUSE-DBH 12, WHICH SERVES ROLL PRESS No. 2
C007366	ATC	Air Pollution Control Device	BAGHOUSE-DBH 10, WHICH SERVES ROLL PRESS No.2
C007367	ATC	Air Pollution Control Device	BAGHOUSE-DBH 11, WHICH SERVES ROLL PRESS No. 2
C007368	ATC	Air Pollution Control Device	MAIN BAGHOUSE, (GBH 3) WHICH SERVES KILN (Q3) AND CLINKER COOLER SYSTEM 3Q
C008244	ATC	Air Pollution Control Device	BAGHOUSE (DBH6)
C008253	PTO	Air Pollution Control Device	BAGHOUSE (EBH9)
C008473	ATC	Air Pollution Control Device	BAGHOUSE - EBH10
C008474	ATC	Air Pollution Control Device	BAGHOUSE - EBH11
C008567	ATC	Air Pollution Control Device	BAGHOUSE (GBH3)
E001910	PTO	Emergency I C E	IC ENGINE, EMERGENCY DIESEL GENERATOR
E004732	PTO	Emergency I C E	IC ENGINE AIR COMPRESSOR, EMERGENCY
N002209	PTO	Gasoline Service Station - Non-Retail GASOLINE DISPENSING FACILITY (NON RETAIL)
T001997	PTO	Tanks (or Silos)	SILO - CLINKER STORAGE (1104)
T001998	PTO	Tanks (or Silos)	SILO - STORAGE
T002210	PTO	Tanks (or Silos)	KILN FUEL
T002211	PTO	Tanks (or Silos)	KILN FUEL
T002212	PTO	Tanks (or Silos)	KILN FUEL
T004582	PTO	Tanks (or Silos)	TANK - WASTE OIL
T007339	ATC	Tanks (or Silos)	RAW MEAL TRANSPORT SYSTEM
T007357	ATC	Tanks (or Silos)	NEW PULVERIZED COAL BIN (FPFB 4)
T008472	ATC	Tanks (or Silos)	SILO-RAW MEAL ES4

PART II

a. While any unit is fired on Public Utilities Commission grade natural gas, Periodic Monitoring for combustion equipment is not required to validate compliance with the Rule 401 Visible Emissions limit. However, the Owner/Operator shall comply with the recordkeeping requirements stipulated elsewhere in this permit regarding the logging of fuel type, amount and suppliers certification information.
b. While any unit is fired on diesel fuel, Periodic Monitoring, in addition to required recordkeeping, is required to validate compliance with Rule 401 Visible Emissions limit as indicated below:
i. Reciprocating engines equal or greater than 1000 horsepower, firing on only diesel with no restrictions on operation a visible emissions inspection is required every three (3) months.
ii. Diesel Standby and emergency reciprocating engines using California low sulfur fuels require no additional monitoring for opacity.
iii. Diesel/Distillate-Fueled Boilers firing on California low sulfur fuels require a visible emissions inspection after every 1 million gallons diesel combusted, to be counted cumulatively over a 5-year period.
iv. On any of the above, if a visible emissions inspection documents opacity, an EPA Method 9 “Visible Emissions Evaluation” shall be completed within 3 working days, or during the next scheduled operating period if the unit ceases firing on diesel/distillate within the 3 working day time frame.

(a) Where the volume discharged is between figures listed in the table, the exact concentration permitted to be discharged shall be determined by linear interpolation.
(b) This condition shall not apply to emissions resulting from the combustion of diesel or PUC quality natural gas fuels in steam generators or gas turbines.
(c) For the purposes of this condition, emissions shall be averaged over one complete cycle of operation or one hour, whichever is the lesser time period.

(a) Where the process weight per hour is between figures listed in the table, the exact weight of permitted discharge shall be determined by linear interpolation.
(b) For the purposes of this condition emissions shall be averaged over one complete cycle of operation or one hour, whichever is the lesser time period.

(a) The provisions of this condition shall not apply to emissions from internal combustion engines.

(a) This condition shall not apply to cases in which the only violation involved is of Section 41700 of the Health and Safety Code, or of District Rule 402.

(a) Any breakdown which results in emissions exceeding a technology-based emission limitation is reported to the District within one hour of such breakdown or within one hour of the time a person knew or reasonably should have known of the occurrence of such breakdown; and
(b) An estimate of the repair time is provided to the District as soon as possible after the report of the breakdown; and
(c) All reasonable steps are immediately taken to minimize the levels of emissions and to correct the condition leading to the excess emissions.
(d) The equipment is operated only until the end of a cycle or twenty-four (24) hours, whichever is sooner, at which time it shall be shut down for repairs unless a petition for an emergency variance has been filed with the clerk of the Hearing Board in accordance with Regulation V.
(e) If the breakdown occurs outside normal District working hours the intent to file an emergency variance shall be transmitted to the District in a form and manner prescribed by the Air Pollution Control Officer.

(a) Organic materials that come into contact with flame or are baked, heat cured or heat polymerized, are limited to 1.4 kilograms (3.1 pounds) per hour not to exceed 6.5 kilograms (14.3 pounds) per day.
(b) Organic materials emitted into the atmosphere from the use of photochemically reactive solvents are limited to 3.6 kilograms (7.9 pounds) per hour, not to exceed 18 kilograms (39.6 pounds) per day, except as provided in Rule 442, subsection (a)(1). All organic materials emitted for a drying period of 12 hours following their application shall be included in this limit.
(c) Organic materials emitted into the atmosphere from the use of non-photochemically reactive solvents are limited to 36.8 kilograms (81 pounds) per hour not to exceed 272 kilograms (600 pounds) per day. All organic materials emitted for a drying period of 12 hours following their application shall be included in this limit.
(d) The provisions of this condition shall not apply to the manufacture of organic solvents, or the transport or storage of organic solvents, or the transport or storage of materials containing organic solvents.
(e) The provisions of this condition shall not apply to the use of equipment for which other requirements are specified by Rules 461, 462, 463, and 464 or which are exempt from air pollution control requirements by said rules.

(i) Cold solvent degreasers using only low volatility solvents which are not agitated, shall operate with a freeboard height of not less than 6 inches.
(ii) Cold solvent degreasers using only low volatility solvents may operate with a freeboard ratio equal to or greater than 0.50 when the cold solvent degreaser has a cover which remains closed during the cleaning operation.
(iii) Any cold solvent degreasers using solvent which is agitated, or heated above 50oC (120oF) shall operate with a freeboard ratio equal to or greater than 0.75.
(iv) A water cover may be used as an acceptable control method to meet the freeboard requirements, when the solvent is insoluble in water and has a specific gravity greater than 1.
(d) Cold Solvent Degreasers - Cover Requirements:
(i) Cold solvent degreasers using high volatility solvent shall have a cover that is a sliding, rolling or guillotine (bi-parting) type which is designed to easily open and close without disturbing the vapor zone.

(ii) A permanent, conspicuous mark locating the maximum allowable solvent level conforming to the applicable freeboard requirements.

(i) Any solvent cleaning equipment and any emission control device shall be operated and maintained in strict accord with the recommendations of the manufacturer.
(ii) Degreasers shall not be operating with any detectable solvent leaks.
(iii) All solvent, including waste solvent and waste solvent residues, shall be stored in closed containers at all times. All containers for any solvent(s) shall have a label indicating the name of the solvent/material they contain.
(iv) Waste solvent and any residues shall be disposed of by one of the following methods: a commercial waste solvent reclamation service licensed by the State of California; or a federally or state licensed facility to treat, store or dispose of such waste; or the originating facility may recycle the waste solvent and materials in conformance with requirements of Section 25143.2 of the California Health and Safety Code.
(v) Degreasers shall be covered to prevent fugitive leaks of vapors, except when processing work or to perform maintenance.
(vi) Solvent carry-out shall be minimized by the following methods:
a) Rack workload arranged to promote complete drainage
b) Limit the vertical speed of the power hoist to 3.3 meters per minute (11 ft/min) or less when such a hoist is used.
c) Retain the workload inside of the vapor zone until condensation ceases.
d) Tip out any pools of solvent remaining on the cleaned parts before removing them from the degreaser if the degreasers are operated manually.
e) Do not remove parts from the degreaser until the parts are visually dry and not dripping/leaking solvent. (This does not apply to an emulsion cleaner workload that is rinsed with water within the degreaser immediately after cleaning.)
(vii) The cleaning of porous or absorbent materials such as cloth, leather, wood or rope is prohibited.
(viii) Except for sealed chamber degreasers, all solvent agitation shall be by either pump recirculation, a mixer, or ultrasonics.
(ix) The solvent spray system shall be used in a manner such that liquid solvent does not splash outside of the container. The solvent spray shall be a continuous stream, not atomized or shower type, unless, the spray is conducted in a totally enclosed space, separated from the environment.
(x) For those degreasers equipped with a water separator, no solvent shall be visually detectable in the water in the separator.
(xi) Wipe cleaning materials containing solvent shall be kept in closed containers at all times, except during use.
(xii) A degreaser shall be located so as to minimize drafts being directed across the cleaning equipment, the exposed solvent surface, or the top surface of the vapor blanket.
(xiii) A method for draining cleaned material, such as a drying rack suspended above the solvent and within the freeboard area, shall be used so that the drained solvent is returned to the degreaser or container.

Any solvent using operation or facility which is not subject to the source-specific Rule 1104 shall comply with the provisions of Rule 442. Any solvent using operation or facility which is exempt from all or a portion of the VOC limits, equipment limits or the operational limits of Rule 1104 shall be subject to the applicable provisions of Rule 442.

Owner/Operator subject to Rule 1104 or claiming any exemption under Rule 1104, Section (E), shall comply with the following requirements:
(1) Maintain and have available during an inspection, a current list of solvents in use at the facility which provides all of the data necessary to evaluate compliance, including the following information separately for each degreaser, as applicable:
(i) product name(s) used in the degreaser, and
(ii) the mix ratio of solvent compounds mixtures of solvents are used, and
(iii) VOC content of solvent or mixture of compounds as used, and
(iv) the total volume of the solvent(s) used for the facility, on a monthly basis, and
(v) the name and total volume applied of wipe cleaning solvent(s) used, on a monthly basis.
(2) Additionally, for any degreaser utilizing an add-on emission control device/system as a means of complying with provisions of Rule 1104 shall, on a monthly basis, maintain records of key system operating and maintenance data. Such data is recorded for the purpose of demonstrating continuous compliance during periods of emission producing activities. The data shall be recorded in a manner as prescribed by the District.
(3) Documentation shall be maintained on site of the disposal or on site recycling of any waste solvent or residues.
(4) Records shall be retained (at facility) and available for inspection by District, state or federal personnel for the previous 5 year period as required by this Title V / Federal Operating Permit.

(a) Electrostatic attraction.
(b) High Volume Low Pressure (HVLP) spray equipment.
(c) Dip coat.

(a) A facility which uses a total of less than one gallon of coating in any one day, including any VOC-containing materials added to the original coating as supplied by the manufacturer.
(b) Total noncompliant coating use per facility that does not exceed 55 gallons per year.
(c) Stencil coatings.
(d) Safety-indicating coatings.
(e) Magnetic data storage disk coatings.
(f) Solid-film lubricants.
(g) Adhesives.
(h) The coating of motor vehicle bodies at motor vehicle rework facilities.

(a) (i) VOC-containing materials for surface preparation shall not have a VOC content in excess of 200 grams of VOC per liter of material (1.67 pounds per gallon); or
(ii) VOC-containing materials has an initial boiling point of 190 deg C (374 deg F) or greater; or
(iii) VOC-containing materials has a total VOC vapor pressure of 20 mm Hg or less, at 20 deg C (68 deg F).
(b) Owner/Operator shall use closed, nonabsorbent containers for the storage or disposal of cloth or paper used for solvent surface preparation and cleanup.
(c) Owner/Operator shall store fresh or spent solvent in closed containers.
(d) Owner/Operator shall not use organic compounds for the cleanup of spray equipment including paint lines unless an enclosed system is used for cleanup. The system shall enclose spray guns, cups, nozzles, bowls, and other parts during washing, rinsing and draining procedures. Equipment used shall minimize the evaporation of organic compounds to the atmosphere.

(a) Owner/Operator shall maintain and have available during an inspection, a current list of coatings in use which provides all of the coating data necessary to evaluate compliance, including the following information, as applicable:
1. coating, catalyst, and reducer used.

3. VOC content of coating as applied.
4. quantity of Group II exempt compounds used.
(b) Owner/Operator shall maintain records on a daily basis including:
1. coating and mix ratio of components used in the coating; and
2. quantity of each coating applied.
(c) Owner/Operator shall maintain records on a daily basis showing the type and amount of solvent used for cleanup, surface preparation, and paint removal.
(d) Records shall be retained (at facility) and available for inspection by District, state or federal personnel for the previous 5 year period as required by this Title V / Federal Operating Permit.

(a) Samples of coatings and solvent as specified in Part II, Conditions A.26 through A.39 shall be analyzed as prescribed by EPA Reference Method 24 for VOC content (without correction for exempt compounds) and ASTM D4457-85, or ARB Method 432 for determination of emissions of exempt compounds. Perfluorocarbon compounds shall be assumed to be absent from a product or process unless a manufacturer or facility Owner/Operator identifies the specific individual compounds (from the broad classes of perfluorocarbon compounds) and the amounts present in the product or process and provides a validated test method which can be used to quantify the specific compounds.
(b) Emissions of volatile organic compounds as specified in Part II, Conditions A.26 through A.39 shall be measured as prescribed by EPA Reference Method 25 for determination of VOC emissions (without correction for exempt compounds) and EPA Method 18, or ARB Method 422 for measuring emission of exempt compounds.
(c) Transfer efficiency as required by Part II, Conditions A.26 through A.39 shall be determined by South Coast Air Quality Management District Spray Equipment Transfer Efficiency Test Procedure for Equipment User, May 24, 1989.
(d) Overall abatement efficiency is the product of capture efficiency as determined by procedures described in 55 FR 26865, 29 June, 1990, and abatement device efficiency.

(a) The VOC content of coatings and solvents, as specified in subsections (C)(2) and (C)(4)(c)(i), shall be analyzed as prescribed by USEPA Reference Method 24 for VOC content (without correction for exempt compounds) and ASTM D4457-85, or CARB Method 432, for determination of emissions of exempt compounds. Perfluorocarbon compounds shall be assumed to be absent from a product or process unless a manufacturer or facility operator identifies the specific individual compounds (from the broad classes of perfluorocarbon compounds) and the amounts present in the product or process and provides a validated test method which can be used to quantify the specific compounds.
(b) Determination of the initial boiling point of liquid containing VOC, subject to subsection (C)(4)(c)(ii), shall be conducted in accordance with ASTM D1078-86.
(c) Calculation of total VOC vapor pressure for materials subject to subsection (C)(4)(c)(iii) shall be conducted in accordance with ASTM D2879-86. The fraction of water and exempt compounds in the liquid phase shall be determined by using ASTM D3792-91 and D4457-85 and shall be used to calculate the partial pressure of water and exempt compounds. The results of vapor pressure measurements obtained using ASTM D2879-86 shall be corrected for partial pressure of water and exempt compounds.
(d) Measurement of solvent losses from alternative application cleaning equipment subject to (C)(4)(b)(iii) shall be conducted in accordance with the South Coast Air Quality Management District's "General Test Method for Determining Solvent Losses from Spray Gun Cleaning Systems" (11/1/94).
(e) Measurement of acid content of a substance shall be determined by ASTM D1613-85.
(f) Measurement of metal content of coatings shall be determined in accordance with South Coast Air Quality Management District's "Laboratory Methods of Analysis for Enforcement Samples" manual, "Determination of Percent Metal in Metallic Coatings by Spectrographic Method, Method 311".
(g) Capture Efficiency shall be determined according to USEPA's technical document, "Guidelines for Determining Capture Efficiency" (1/9/95).
(h) The control efficiency of the Control Device shall be determined according to USEPA Test Methods 25, 25A or 25B for measuring the total gaseous organic concentrations at the inlet and outlet of the emissions Control Device, as contained in 40 CFR Part 60, Appendix A. USEPA Test Method 18 or CARB Method 422 shall be used to determine emissions of exempt compounds.
(i) Measurement of solids content by weight of a substance shall be conducted in accordance with ASTM D1475-60.
(j) Alternative test methods may be used upon obtaining the approval of the APCO, CARB and USEPA.
(k) Demonstration of Transfer Efficiency of alternative application methods subject to subsection (C)(1)(a)(v) shall be conducted in accordance with South Coast Air Quality Management District's "Spray Equipment Transfer Efficiency Test Procedure for Equipment User" (5/24/89).

(a) The cumulative annual usage of each fuel type. The cumulative annual usage of each fuel type shall be monitored from utility service meters, purchase or tank fill records.
(b) Fuel suppliers’ fuel analysis certification/guarantee including fuel sulfur content shall be kept on site and available for inspection by District, state or federal personnel upon request. The sulfur content of diesel fuel shall be determined by use of ASTM method D2622-82, or (ASTM method D 2880-71, or equivalent). Vendor data meeting this requirement is sufficient.

(a) Summary of deviations from any federally-enforceable requirement in this permit.
(b) Summary of all emissions monitoring and analysis methods required by any Applicable Requirement / federally - enforceable requirement.
(c) Summary of all periodic monitoring, testing or record keeping (including test methods sufficient to yield reliable data) to determine compliance with any Applicable Requirement / federally - enforceable requirement that does not directly require such monitoring.
(d) Summary of necessary requirements concerning use and maintenance of equipment including the installation and maintenance of monitoring equipment.

(a) For deviations involving emissions of air contaminants in excess of permit conditions including but not limited to those caused by a breakdown, prompt reporting shall be within one hour of the occurrence of the excess emission or within one hour of the time a person knew or reasonably should have known of the excess emission. Documentation and other relevant evidence regarding the excess emission shall be submitted to the District within sixty (60) days of the date the excess emission was reported to the District. [SIP Pending: Rule 430 - Breakdown Provisions as amended 12/21/94 and submitted 2/24/95]

(a) A narrative description of how the facility will achieve compliance with such requirements; and
(b) A Schedule of Compliance which contains a list of remedial measures to be taken for the facility to come into compliance with such requirements, an enforceable sequence of actions, with milestones, leading to compliance with such requirements and provisions for the submission of Progress Reports at least every six (6) months. The Schedule of Compliance shall include any judicial order, administrative order, and/or increments of progress or any other schedule as issued by any appropriate judicial or administrative body or by the District Hearing Board pursuant to the provisions of Health & Safety Code §42350 et seq.; and
(c) Progress Reports submitted under the provisions of a Schedule of Compliance shall include: Dates for achieving the activities, milestone, or compliance required in the schedule of compliance; and dates when such activities, milestones or compliance were achieved; and an explanation of why any dates in the schedule of compliance were not or will not be met; and any preventive or corrective measures adopted due to the failure to meet dates in the schedule of compliance.

PART III