250-RICR-120-05-32
250-RICR-120-05-32. Control of Volatile Organic Compounds from Marine Vessel Loading Operations (version Technical Revision, 07/19/2007 to 01/04/2022)
32.1 Purpose
The purpose of this
regulation is to limit volatile organic compound emissions from
marine vessel loading operations.
32.2 Authority
These regulations are
authorized pursuant to R.I. Gen. Laws § 42-17.1-2(19) and Chapter
23-23, and have been promulgated pursuant to the procedures set forth
in the R.I. Administrative Procedures Act, R.I. Gen. Laws Chapter
42-35.
32.3 Application
The terms and provisions of
this regulation shall be liberally construed to permit the Department
to effectuate the purposes of state laws, goals and policies.
32.4 Severability
If any provision of this
regulation or the application thereof to any person or circumstance,
is held invalid by a court of competent jurisdiction, the validity of
the remainder of the regulation shall not be affected thereby.
32.5 Definitions
A. Unless otherwise expressly
defined in this section, the terms used in this regulation shall be
defined by reference to (General Definitions), Part 0 of this
Subchapter. As used in this regulation, the following terms shall,
where the context permits, be construed as follows:
1. "Combustion device"
means emission control equipment used for combustion or destruction
of organic vapors and includes, but is not limited to, thermal
incinerators, catalytic incinerators, flares, boilers, and process
heaters.
2. "Emission control
equipment" means any equipment, machinery, apparatus, or device
used to recover or reduce emissions of volatile organic compounds.
3. "Gasoline" means
any petroleum distillate having a Reid vapor pressure of more than 4
psia as determined by ASTM Method D323. This term includes but is
not limited to mixtures of alcohols and gasoline.
4. "Leak free" means
the dripping of a liquid containing volatile organic compounds at a
rate of four drops per minute or less; or an emission of gaseous
volatile organic compounds which causes an appropriate analyzer
sampling one centimeter or less from a source to register less than
10,000 ppm as methane.
5. "Loading event"
means an incident or occurrence beginning with the connecting of
marine terminal storage tanks to a marine tank vessel by means of
pipes or hoses followed by the transferring of organic liquid cargo
and ending with the disconnecting of the pipes or hoses; or any means
of admitting any other liquid into a marine vessel's cargo tanks.
Loading events shall include only such incidents which occur when a
marine tank vessel is moored to a dock or other permanent stationary
structure.
6. "Marine tank vessel"
means any marine vessel which is specially constructed or converted
to carry liquid bulk cargo in tanks.
7. "Marine terminal"
means any facility, equipment, or structure constructed to load or
unload organic liquid bulk cargo into or out of marine tank vessels.
8. "Marine vessel"
means any tugboat, tanker, freighter, passenger ship, barge or other
boat, ship or water craft except those used primarily for recreation.
9. "Organic liquid"
means, for the purposes of this regulation, gasoline, gasoline
blending stocks, aviation gas and aviation fuel which contains
gasoline, such as JP-4 type.
10. "Recovery device"
means emission control equipment used to remove organic vapors and
recover liquids or chemicals and includes, but is not limited to,
absorbers, carbon absorbers, and condensers.
11. "Segregated
ballasting operations" means the loading of ballast water into
tanks on a marine vessel if those tanks are used only for ballasting
and never hold organic liquid.
12. "Vapor tight marine
vessel" means a marine vessel which has been demonstrated within
the previous 12 months to have no leaks. A marine vessel loaded at
negative pressure is assumed to be vapor tight for the purposes of
this regulation. Discharges from pressure/vacuum relief valves on
cargo tank vent lines are not considered leaks for the purposes of
this definition.
32.6 Applicability
A. The provisions of this
regulation apply to any loading event in which organic liquid is
loaded into marine tank vessels and to loading events in which any
liquid is loaded into a marine vessel's cargo tanks if the most
recent cargo held in those tanks was an organic liquid. This
regulation does not apply to segregated ballasting operations.
B. Wherever the term Volatile
Organic Compound or VOC is used in §§ 32.6 through 32.10 of this
Part, this term should be read as Volatile Organic Compound and
Halogenated Organic Compound or VOC and HOC.
32.7 Emission Limitations
A. A loading event shall not
be conducted unless one of the following conditions is met:
1. Volatile organic compounds
emissions do not exceed 5.7 grams per cubic meter (2 pounds per 1000
barrels) of liquid loaded into the marine tank vessel, or,
2. The emissions of volatile
organic compounds are reduced by at least 95 percent by weight from
uncontrolled conditions if a recovery device is used and by at least
98 percent by weight from uncontrolled conditions if a combustion
device is used.
B. All of a marine terminal's
hatches, pressure relief valves, connections, gauging ports and vents
which are used in connection with a loading event shall be leak free.
C. A loading event shall not
be conducted unless the receiving marine vessel is vapor tight. To
determine whether a marine vessel is vapor tight, the owner or
operator of the marine terminal must follow the following procedures
for each loading event, with the exception of loading events
performed at a negative pressure:
1. Obtain a copy of the record
of the most recent pressure test or leak test on the receiving marine
vessel. The record must contain all information specified in §
32.8(B) of this Part.
2. If, according to the
records obtained pursuant to the requirements of § 32.7(C)(1) of
this Part, the marine vessel passed the most recent pressure or leak
test and that test was performed within the previous 12 month period,
the vessel shall be considered vapor tight.
3. If, according to the
records obtained pursuant to the requirements of § 32.7(C)(1) of
this Part, the marine vessel failed its most recent leak or pressure
test, no loading event shall be conducted unless the operator of the
marine vessel provides written documentation that all leaks have been
repaired subsequent to the failed test. Any loading event involving
a marine vessel that has been repaired subsequent to failing its most
recent leak or pressure test must be conducted in conjunction with
the performance of a leak test, as specified in § 32.7(C)(4) of this
Part.
4. If, according to the
records obtained pursuant to the requirements of § 32.7(C)(1) of
this Part, the marine vessel has not passed a leak or pressure test
within the previous 12 month period, a leak test of the vessel shall
be performed during the loading event. No loading events shall be
performed if the vessel failed its most recent leak test or pressure
test and does not provide the owner or operator of the marine
terminal with documentation that shows that all leaks subsequently
have been repaired, as specified in § 32.7(C)(3) of this Part.
5. A person testing a marine
vessel to determine whether that vessel is vapor tight shall provide
the operator of the marine vessel and the owner or operator of the
marine terminal with documentation of the test which includes all
information specified in § 32.8(B) of this Part.
32.8 Recordkeeping and Recording
A. The owner or operator of a
marine terminal loading facility shall record the following
information about each loading event and maintain this information at
the facility for a period of five years:
1. The location of the loading
event,
2. The company responsible for
conducting the loading event,
3. The date and time at which
the marine vessel arrived and departed from the location of the
loading event,
4. The name, registry of
vessels and name and address of the legal owner of the marine tank
vessel participating in the loading event,
5. The prior cargo carried by
the receiving marine tank vessel,
6. The type and amount of
liquid cargo loaded into the receiving marine tank vessel,
7. The condition of the
receiving tanks prior to being loaded (i.e. cleaned, crude oil,
washed, gas freed, etc.),
8. The amount of ballast water
added to a marine vessel's tanks, except for ballast water used in
segregated ballasting operations, and,
9. A description of procedures
used to prevent venting.
B. The owner or operator of a
marine terminal shall maintain at the facility for a period of five
(5) years a record of the most recent leak test or pressure test
conducted on a marine vessel prior to or in conjunction with each
loading event. Such records shall be made available to the
Department or to EPA on request and shall include the following
information:
1. Test method;
2. Marine vessel owner and
address;
3. Marine vessel
identification number;
4. Date and location of test;
5. Tester's name and
signature;
6. Witnessing inspector's
name, signature and affiliation; and,
7. Test results.
C. The owner or operator of a
marine terminal at which loading events subject to this regulation
are conducted shall collect and record the following information and
maintain the information at the facility for a period of five
(5) years. These records shall be made available to the
Department and EPA upon request.
1. The date and results of
each emission test performed at the facility as required in §
32.9(A) of this Part and of each leak free determination performed as
required in § 32.9(B) of this Part;
2. A daily log of operating
time for any capture system, emission control equipment, and
monitoring equipment;
3. A maintenance log for any
capture system, emission control equipment, and monitoring equipment
detailing all routine and non-routine maintenance performed,
including dates and duration of any outages;
4. A maintenance log for all
of the marine terminal's hatches, pressure relief valves,
connections, gauging ports and vents which are used in connection
with loading events, including dates when leaks were repaired;
5. The dates of any loading
events which bypassed the emission control equipment or which were
performed when the marine terminal was not leak free;
6. For thermal incinerators:
a. All 3‑hour periods of
operation in which the average combustion temperature was more than
28ºC (50ºF) below the average combustion temperature during the
most recent performance test that demonstrated that the facility was
in compliance, and,
b. The operating temperature.
7. For catalytic incinerators:
a. All periods where the
temperature increase across the catalyst bed is less than 80% of the
temperature increase recorded during the most recent performance test
that demonstrated that the facility was in compliance, and,
b. The inlet and outlet
temperatures and temperature rise across the catalyst bed.
8. For carbon adsorbers:
a. All 3-hour periods of
operation during which the average VOC concentration or reading of
organics in the exhaust gases is more than 20 percent greater than
the average exhaust gas concentration or reading measured by the
organics monitoring device during the most recent determination of
the recovery efficiency of the carbon adsorber that demonstrated that
the facility was in compliance, and,
b. The pressure drop across
the adsorber and the hydrocarbon levels for breakthrough.
32.9 Compliance
Demonstration/Testing
A. Compliance with the
emission limitations of § 32.7(A) of this Part shall be demonstrated
upon startup of the emission control equipment and thereafter upon
request of the Director in accordance with 40 C.F.R. § 60, Appendix
A, Method 25 as amended or another EPA approved method which has been
accepted by the Director. This test shall be conducted so that at
least 50% of the total liquid loaded is included.
B. Leak free determinations at
marine terminals shall be made upon startup of the emission control
equipment and monthly thereafter. Gaseous leaks shall be measured in
accordance with EPA Reference Method 21 or another method which has
been accepted by the Director and by EPA.
C. Any leak test or pressure
test used to demonstrate that a marine vessel is vapor tight shall
utilize a method which has been accepted by the Director and by EPA.
D. The owner or operator of a
marine terminal shall notify the Director of the date of any test
demonstrating the control efficiency of emission control equipment at
least 90 days in advance of that date. If required by the
Department, a sampling protocol shall be submitted at least 60 days
in advance of the testing date. Testing results shall be submitted
to the Office of Air Resources within 30 days of completion of the
test.
32.10 Compliance Schedules
A. Any marine terminal at
which a loading event subject to this regulation is conducted shall
be in compliance with the provisions of §§ 32.7 and 32.8 of this
Part on and after January 1, 1996.
B. The owner or operator of
any marine terminal at which loading events subject to this
regulation are conducted shall, by July 30, 1994, submit to the
Director a compliance plan which describes the steps and schedule
that will be taken to achieve compliance with this regulation.
C. Any compliance plan which
includes equipment replacement or modification or installation of
emission control equipment shall provide for periodic increments of
progress, including but not limited to:
1. Date by which engineering
plans and permit applications will be submitted,
2. Date by which equipment
will be ordered,
3. Installation date after
confirmation of order by the manufacturer, and,
4. Date by which the
applicable regulatory emission limitations will be achieved after
equipment is in satisfactory operation.
D. No compliance schedule
submitted to satisfy the requirements of this section shall allow a
facility to exceed any applicable emission limitations including but
not limited to:
1. Best Available Control
Technology determinations, or,
2. Lowest Achievable Emissions
Rate determinations, or,
3. Federal New Source
Performance Standards codified at 40 C.F.R. § 60, or National
Emission Standards for Hazardous Air Pollutants, codified at 40
C.F.R. § 61 or § 63, or,
4. Any other condition or
standard that is specifically required by the Clean Air Act (as
amended) for new or modified sources.
E. Compliance schedules
submitted in accordance with the requirements of this section are
subject to review and approval by the Director.