SOUTH COAST AIR QUALITY MANAGEMENT DISTRICT
RULE 1110.2 - EMISSIONS
FROM GASEOUS- AND LIQUID-FUELED ENGINES
(Adopted August 3,
1990)(Amended September 7, 1990)(Amended August 12, 1994)(Amended December 9,
1994)(Amended November 14, 1997)
(a) Purpose
The purpose
of Rule 1110.2 is to reduce Oxides of Nitrogen (NOx), Volatile
Organic Compounds (VOCs), and Carbon Monoxide (CO) from engines.
(b) Applicability
All stationary and portable engines over 50 bhp
are subject to this rule.
(c) Definitions
For the purpose of this rule, the following
definitions shall apply:
(A) Is used in or on a piece of equipment that is self-propelled or serves a dual purpose by both propelling itself and performing another function (such as a mobile crane); or
(B) Is used in or on a piece of equipment that is intended to be propelled while performing its function (such as lawn mowers and string trimmers); or
(C) By itself, or in or on a piece of equipment, is portable or transportable, meaning designed to be and capable of being carried or moved from one location to another. Transportability includes, but is not limited to, wheels, skids, carrying handles, dolly, trailer, platform or mounting.
An engine is not portable if:
(A) the engine or its replacement remains
or will reside at the same location for more than 12 consecutive months. Any
engine, such as a back-up or stand-by engine, that replaces an engine at a
location and is intended to perform the same function as the engine being
replaced, will be included in calculating the consecutive time period. In that
case, the cumulative time of both engines, including the time between the
removal of the original engine and installation of the replacement engine,
will be counted toward the consecutive time period; or
(B) the engine remains or will reside at a location for less than 12 consecutive months where such a period represents the full length of normal annual source operations such as a seasonal source; or
(C) the engine is removed from one location for a period and then it or its equivalent is returned to the same location thereby circumventing the portable engine residence time requirements.
The period during which the engine is maintained at a designated storage facility shall be excluded from the residency time determination.
(d) Requirements
(A) Remove such engine permanently from service or replace the engine with an electric motor, or
(B) Reduce emissions from such engine, in accordance with the compliance schedule in paragraph (e)(1), to the compliance limits listed in TABLE I.
|
TABLE I COMPLIANCE LIMITS | ||
|
NOx |
VOC |
CO |
|
(ppm)1 |
(ppm)1, 2 |
(ppm)1 |
(C) Notwithstanding the provisions in subparagraph (d)(1)(B), the owner or operator of any stationary engines described in Table II may, in lieu of conversion to electrical power or permanent engine removal, reduce the engine CO emissions to no more than 2000 ppm by volume corrected to 15 percent oxygen on a dry basis and averaged over 15 minutes, and reduce the emissions of NOx, and VOC measured as methane, from such engines to the compliance limit specified by the following formula:
|
COMPLIANCE LIMIT FORMULA | ||||
| Compliance Limit |
= |
Reference Limit |
x |
EFF |
|
25% | ||||
| Where: | ||
| Compliance Limit | = | the allowable NOx, or VOC emission limit (ppm by volume) corrected to 15 percent oxygen on a dry basis, and averaged over 15 consecutive minutes. |
| Reference Limit | = | the NOx or VOC emission limit (ppm by volume) corrected to 15 percent oxygen on a dry basis. The reference limits for various bhp ratings (continuous rating by the manufacturer) are listed in TABLE III. |
|
TABLE II STATIONARY ENGINES DESCRIPTION |
| For electric power generation |
| Fired by landfill gas |
| Fired by sewage digester gas |
| Used to drive a water supply or conveyance pump except for aeration facilities |
| Fired by oil field-produced gas |
| For integral engine-compressor applications operating less than 4000 hours per calendar year |
| Fired by liquefied petroleum gas (LPG) |
|
TABLE III REFERENCE LIMITS, ppm | ||
|
Bhp Rating |
NOx |
VOC |
| 500 and greater |
36 |
250 |
| Greater Than 50 and Less Than 500 |
45 |
250 |
(A) By December 31, 1999, reduce emissions from such engine to the applicable requirements of TABLE IV for spark-ignition engines, or TABLE V for compression-ignition engines;
(B) By January 1, 2010, meet the most stringent emissions standard which is the applicable emissions standard in effect and set forth in Title 13 of the California Code of Regulations for that engine rating. If no emissions standard exists under the California Code of Regulations, then the applicable emissions standard set forth in CFR 40 Part 89 shall apply. If no standard exists under the California Code of Regulations and CFR 40 Part 89, then the applicable requirements of TABLE IV for spark-ignition engines or TABLE V for compression-ignition engines shall apply; and
(C) Submit to the Executive Officer a letter certifying that the engine is in compliance with the provisions of the paragraph, in accordance with the compliance schedule in paragraph (e)(2).
|
TABLE IV | ||
|
NOx |
VOC |
CO |
|
80 ppm3 (1.5 g/bhp-hr) |
240 ppm3 (1.5 g/bhp-hr) |
176 ppm3 (2.0 g/bhp-hr) |
|
TABLE V | |
|
Rated Brake Horsepower |
Requirements |
| Greater Than 50 And Less Than 117 | 770 ppm4 NOx (10.0 g/bhp-hr), or turbocharger and 4-degree injection timing retard |
| Greater Than or Equal To 117 And Less Than 400 | 550 ppm4 NOx (7.2 g/bhp-hr), or turbocharger and aftercooler/intercooler and 4-degree injection timing retard |
| Greater Than or Equal To 400 | 535 ppm4 NOx (7.0 g/bhp-hr), or turbocharger and aftercooler/intercooler and 4-degree injection timing retard |
(e)Compliance
(A) Owners/operators of stationary engines with an amended Rule 1110.1 Emission Control Plan submitted by July 1, 1991, or an Approved Emission Control Plan, designating the permanent removal of engines or the replacement of engines with electric motors, in accordance with subparagraph (d) (1)(A), shall do so by December 31, 1999, or reduce the emissions from the engines to the limits listed in Table VI in accordance with the following schedule:
(ii) By September 30, 1999, initiate control equipment installation; and
(iii) By December 31, 1999, have the engine under compliance.
|
TABLE VI ALTERNATIVE TO ELECTRIFICATION | ||
|
NOx |
VOC |
CO |
|
0.15 g/bhp-hr |
0.15 g/bhp-hr |
0.6 g/bhp-hr |
(B) Owners/operators of stationary engines that were altered to come into compliance with subparagraph (c)(1)(A) or paragraph (c)(2) of Rule 1110.1 by August 3, 1990, or stationary engines originally installed to effect compliance with and/or meet the limits in subparagraph (c)(1)(A) or paragraph (c)(2) of Rule 1110.1 by August 3, 1990, shall:
(II) By September 30, 2004, initiate engine modification or control equipment installation; and
(III) By December 31, 2004, be in compliance with subparagraph (d)(1)(B) or (d)(1)(C) of this rule as appropriate.
(II) By September 30, 2004, initiate engine modification or control equipment installation; and
(III) By December 31, 2004, have engines under compliance.
(C) Except as specified in subparagraph (e)(1)(B), or otherwise specified in an Approved Emission Control Plan or amended Rule 1110.1 Emission Control Plan submitted by July 1, 1991:
(ii) Any stationary engine installed after December 31, 1994 but prior to November 14, 1997 shall be in compliance with the provisions of subparagraph (d)(1)(B), or (d)(1)(C) as appropriate before being placed into service.
The owner/operator of portable engines subject to the provisions of subparagraph (d)(2) shall:
(A) For engines for which engine modification or add-on control is used to comply with the applicable requirements of TABLE IV for spark-ignition engines, or TABLE V for compression-ignition engines :
(ii) By September 30, 1999, initiate engine modification or control equipment installation; and
(iii) By December 31, 1999, have engines in compliance with the applicable requirements of TABLE IV for spark-ignition engines, or TABLE V for compression-ignition engines.
(C) For engines for which engine modification or add-on control is used to comply with the most stringent emissions standard as set forth in subparagraph (d)(2)(B):
(ii) By September 30, 2009, initiate engine modification or control equipment installation; and
(iii) By December 31, 2009, have engines in compliance with the most stringent emissions standard.
(f) Monitoring and Recordkeeping
(A) For engines of 1000 bhp and greater, and operating more than two million bhp-hr per calendar year, install, operate and maintain in calibration a NOx continuous emission monitoring system (CEMS) to demonstrate compliance with the emission limits of this rule. CEMS shall meet the requirements described in 40 CFR Part 60, particularly those in Appendix B, Spec. 2 and Appendix F, as well as the reporting requirements of CFR Part 60.7(c), 60.7(d), and 60.13, and shall include equipment that measures and records NOx exhaust gas concentrations, corrected to 15 percent oxygen on a dry basis.
The owner/operator of an engine that is required to install CEMS may
request the Executive Officer to approve an alternative monitoring device (or
system components) to demonstrate compliance with the emission limits of this
rule. The applicant shall demonstrate to the Executive Officer that the
proposed alternative monitoring device is at a minimum equivalent in relative
accuracy, precision, reliability, and timeliness to a CEMS for that engine,
according to the criteria specified in 40 CFR Part 75 Subpart E. In lieu of
the criteria specified in 40 CFR Part 75 Subpart E, substitute criteria is
acceptable if the applicant demonstrates to the Executive Officer that the
proposed alternative monitoring device is at minimum equivalent in relative
accuracy precision, reliability, and timeliness to a CEMS for that engine.
Upon approval by the Executive Officer, the substitute criteria shall be
submitted to the federal Environmental Protection Agency (EPA) as an amendment
to the State Implementation Plan (SIP).
If the alternative monitoring
device is denied or fails to be recertified, a CEMS shall be required.
(B) For engines subject to the provisions of subparagraph (f)(1)(A), the monitoring system shall have data gathering and retrieval capability approved by the Executive Officer. Data shall be maintained for at least two years and made available for inspection by the Executive Officer.
(C) The engine shall have an operational non-resettable totalizing time meter to determine the engine elapsed operating time.
(D) Provide source test information regarding the exhaust gas, specifically for NOx, VOC reported as methane, and CO concentrations (concentrations in ppm by volume, corrected to 15 percent oxygen on dry basis) at least once every 3 years. If the engine has not been operated within three months of the date a source test is required, the source test shall be conducted when the engine resumes operation for a period longer than either seven consecutive days or 15 cumulative days of operation. The owner/operator of the engine shall keep sufficient operating records to demonstrate that it meets the requirements for extension of the source testing deadlines.
(E) Maintain a monthly engine operating log that includes:
(ii) Type of liquid and/or type of gaseous fuel;
(iii) Fuel consumption (cubic feet of gas or gallons of liquid); and
(iv) Cumulative hours of operation since the last source test required in subparagraph (f)(1)(D).
The log shall be available for inspection at any time.
The owner/operator of any portable engine subject to the provisions of paragraph (d)(2) shall maintain a monthly engine operating log that includes:
(A) Total hours of operation;
(B) Type of liquid and/or type of gaseous fuel; and
(C) Fuel consumption (cubic feet of gas or gallons of liquid).
The log
shall be available for inspection at any time.
(g) Test Method
Testing to verify compliance with the applicable
requirements shall be conducted in accordance with the test methods specified in
TABLE VII, or any test methods approved by the California Air Resources Board
(CARB) and EPA, and authorized by the Executive Officer.
|
TABLE VII TESTING METHODS | |
|
Pollutant |
Method |
|
NOx |
EPA Test Method 20 or District Method 100.1 |
|
CO |
EPA Test Method 10 or District Method 100.1 |
|
VOC |
EPA Test Method 25 or District Method 25.1* |
A violation of any standard of this rule established by any of the specified test methods, or any test methods approved by the CARB or EPA, and authorized by the Executive Officer, shall constitute a violation of this rule.
(h)Technology Assessment for PM2.5
The Executive
Officer shall, by December 31, 1999, conduct a technology assessment to
determine relative contribution of the engines, which operate for the
manufacture of snow and/or operation of ski lifts, to potential PM2.5
violations, and report to the Governing Board with recommended actions to be
taken, if necessary, to ensure PM2.5 standard compliance. In
conducting the assessment, the Executive Officer shall consider any applicable
future CARB surveys on PM2.5 emissions.
(i) Exemptions
The provisions of subdivision (d) shall not apply
to: