SOUTH COAST AIR QUALITY MANAGEMENT DISTRICT
RULE 1142 - MARINE TANK VESSEL OPERATIONS
(Adopted July 19, 1991)
(a) Applicability
This rule shall apply to all loading, lightering, ballasting, and housekeeping events where a marine tank vessel is filled with an organic liquid; or where a liquid is placed into a marine tank vessel's cargo tanks which had previously held organic liquid.
(b) Definitions
(A) Group I
chlorodifluoromethane (HCFC-22)
dichlorotrifluoroethane (HCFC-123)
tetrafluoroethane (HFC-134a)
dichlorofluoroethane (HCFC-141b)
chlorodifluoroethane (HCFC-142b)
(B) Group II
methylene chloride
1,1,1-trichloroethane (methyl chloroform)
trifluoromethane (FC-23)
trichlorotrifluoroethane (CFC-113)
dichlorodifluoromethane (CFC-12)
trichlorofluoromethane (CFC-11)
dichlorotetrafluoroethane (CFC-114)
chloropentafluoroethane (CFC-115)
In the future, the use of Group II compounds may be regulated by the District because they are toxic or potentially toxic, upper atmospheric ozone depleters, or cause other environmental impacts. The District Board has adopted a policy which states that chlorofluorocarbons (CFC) will be phased out at the earliest practicable date on or before 1997.
(c) Requirements
(A) Effective January 1, 1992, an owner or operator of a marine tank vessel equipped with emission control equipment shall operate such equipment while conducting a loading, lightering, ballasting, or housekeeping event in South Coast Waters.
(B) Effective January 1, 1994 a loading, lightering, ballasting, or housekeeping event shall not be conducted while in South Coast Waters, unless:
(i) The emissions of volatile organic compounds are limited to 5.7 grams per cubic meter (2 lbs per 1,000 barrels) of liquid loaded into a marine tank vessel; or
(ii) The emissions of volatile organic compounds are reduced by at least 95 percent by weight from uncontrolled conditions.
Effective January 1, 1994, all hatches, pressure relief valves, connections, gauging ports and vents, and other equipment associated with a loading, lightering, ballasting, or housekeeping event shall be maintained free of liquid or gaseous leaks. Any liquid or gaseous leak shall be tagged upon detection and repaired within 4 hours of detection by the owner or operator. Any liquid or gaseous leak detected by District staff shall constitute a violation of this rule.
The emission control equipment shall be designed and operated to collect, store, and process all emissions of volatile organic compounds resulting from a loading, lightering, ballasting, or housekeeping event.
(d) Compliance Schedule
Any owner or operator of a marine tank vessel or a terminal shall submit to the District Executive Officer an application for a Permit to Construct by April 1, 1992, for any equipment required to comply with the provisions of this rule.
(e) Test Methods
Emissions of volatile organic compounds specified in subparagraph (c)(1)(B) shall be measured according to the Environmental Protection Agency's (EPA) Reference Method 25, Air Resources Board's (ARB) Method 2-4, District's Source Test Manual Method 25.1 (March 1989), or any other test method determined to be equivalent after review by the staffs of the District, the Air Resources Board, and the United States Environmental Protection Agency, and approved in writing by the District Executive Officer. This test shall be conducted for at least 30 minutes during the transfer of the last 50 percent of total liquid cargo. For events of less than one hour duration, the test shall include the entire last 50 percent of total liquid cargo.
Emissions of exempt compounds shall be measured according to Air Resources Board Method 422 adopted January 22, 1987, or any other test method determined to be equivalent after review by the staffs of the District, the Air Resources Board, and the United States Federal Environmental Protection Agency and approved in writing by the District Executive Officer.
Mass emission rates of vapor processing systems specified in subparagraph (c)(1)(B) shall be determined according to EPA's Reference Method 25, ARB's Method 2-4, District's Source Test Manual Method 25.1 (March 1989) or any other test method determined to be equivalent after review by the staffs of the District, the Air Resources Board, and the United States Environmental Protection Agency, and approved in writing by the District Executive Officer.
The screening of equipment for gaseous leaks shall be conducted according to EPA's Reference Method 21 or the procedures in the District's Source Test Manual, or any other test method determined to be equivalent after review by the staffs of the District, the Air Resources Board, and the United States Environmental Protection Agency, and approved in writing by the District Executive Officer.
Emissions determined to exceed any limits established by this rule through the use of any of the above-referenced test methods shall constitute a violation of this rule.
(f) Safety and Emergency
Nothing in this rule shall be construed as to:
(g) Notice
Effective January 1, 1992, any owner or operator of a marine tank vessel intending to engage in a loading, lightering, ballasting, or housekeeping event shall notify the District Executive Officer in writing, or by telephone, or in person at least 48 hours prior to the event. Such notice shall include name(s) of marine tank vessel(s), description of operation(s), cargo, location, and estimated start time and duration of the event.
(h) Recordkeeping
Effective January 1, 1994, any owner or operator of a marine tank vessel shall maintain two sets of records regarding each loading, lightering, ballasting, or housekeeping event. One set of records will be kept on board the marine tank vessel and the other set shall be kept at the marine terminal. Records shall be maintained for at least two years and shall be made available to District staff upon request. Such records shall be submitted annually on standard forms specified by the District, and shall contain all information required on the form. The records shall include, but are not limited to, all of the following information:
(i) Ozone Episode Days
Any marine vessel or terminal operator, who has been subject to the prohibition of paragraph (i)(1) for two consecutive days, may conduct a marine loading, lightering, ballasting, or housekeeping event in South Coast Waters for up to three days following the two consecutive days of prohibition.
CALIFORNIA COASTAL WATERS
California Coastal Waters have been defined as that area between the California Coastline and a line starting at
the California-Oregon border at the Pacific Ocean 
thence to 42.0oN 125.5oW
thence to 41.0oN 125.5oW
thence to 40.0oN 125.5oW
thence to 39.0oN 125.0oW
thence to 38.0oN 124.5oW
thence to 37.0oN 123.5oW
thence to 36.0oN 122.5oW
thence to 35.0oN 121.5oW
thence to 34.0oN 120.5oW
thence to 33.0oN 119.5oW
thence to 32.5oN 118.5oW
and ending at the California-Mexico border at the Pacific Ocean.
Boundary of California Coastal Waters
NOTE: Coordinates shown
above are exact. Distances
of California Coastal Waters
boundary from coast are rough
approximations.
Source: Air Resources Board staff.
68 mi 102 mi 27 56 mi
58 mi 79 mi mi
82 mi 35 mi 90 mi