Appendix B to Part 155 - Determining and Evaluating Required Response Resources for Vessel Response Plans
33:2.0.1.5.24.12.179.1.6 : Appendix B
Appendix B to Part 155 - Determining and Evaluating Required
Response Resources for Vessel Response Plans 1. Purpose
1.1 The purpose of this appendix is to describe the procedures
for identifying response resources to meet the requirements of
subparts D, E, F, G, and J of this part. These guidelines will be
used by the vessel owner or operator in preparing the response plan
and by the Coast Guard to review vessel response plans. Response
plans submitted under subparts F and G of this part will be
evaluated under the guidelines in section 2 and Table 1 of this
appendix.
2. Equipment Operability and Readiness
2.1 All equipment identified in a response plan must be capable
of operating in the conditions expected in the geographic area in
which a vessel operates. These conditions vary widely based on the
location and season. Therefore, it is difficult to identify a
single stockpile of response equipment that will function
effectively in every geographic location.
2.2 Vessels storing, handling, or transporting oil in more than
one operating environment as indicated in Table 1 must identify
equipment capable of successfully functioning in each operating
environment. For example, vessels moving from the ocean to a river
port must identify appropriate equipment designed to meet the
criteria for transiting oceans, inland waterways, rivers, and
canals. This equipment may be designed to operate in all of these
environments or, more likely, different equipment may be designed
for use in each area.
2.3 When identifying equipment for response plan credit, a
vessel owner or operator must consider the inherent limitations in
the operability of equipment components and response systems. The
criteria in Table 1 of this appendix must be used for evaluating
the operability in a given environment. These criteria reflect the
general conditions in certain operating areas.
2.4 Table 1 of this appendix lists criteria for oil recovery
devices and boom. All other equipment necessary to sustain or
support response operations in a geographic area must be designed
to function in the same conditions. For example, boats which deploy
or support skimmers or boom must be capable of being safely
operated in the significant wave heights listed for the applicable
operating environment. The Coast Guard may require documentation
that the boom identified in a response plan meets the criteria in
Table 1 of this appendix. Absent acceptable documentation, the
Coast Guard may require that the boom be tested to demonstrate that
it meets the criteria in Table 1 of this appendix. Testing must be
in accordance with certain American Society for Testing Materials
(ASTM) standards [ASTM F 715 (incorporated by reference, see §
155.140) Standard Methods of Testing Spill Control Barrier Membrane
Materials], or other tests approved by the Coast Guard.
2.5 A vessel owner or operator must refer to the applicable Area
Contingency Plan to determine if ice, debris, and weather-related
visibility are significant factors in evaluating the operability of
equipment. The Area Contingency Plan will also identify the average
temperature ranges expected in a geographic area in which a vessel
operates. All equipment identified in a response plan must be
designed to operate within those conditions or ranges.
2.6 The requirements of subparts D, E, F, G, and J of this part
establish response resource mobilization and response times. The
location where the vessel operates farthest from the storage
location of the response resources must be used to determine
whether the resources are capable of arriving on scene within the
time required. A vessel owner or operator must include the time for
notification, mobilization, and travel time of resources identified
to meet the maximum most probable discharge and Tier 1 worst case
discharge requirements. For subparts D and E of this part, Tier 2
and 3 resources must be notified and mobilized as necessary to meet
the requirements for arrival on scene. An on-water speed of 5 knots
and a land speed of 35 miles per hour is assumed, unless the vessel
owner or operator can demonstrate otherwise.
2.7 For subparts D, E, and J of this part, in identifying
equipment, the vessel owner or operator must list the storage
location, quantity, and manufacturer's make and model, unless the
oil spill removal organization(s) providing the necessary response
resources have been evaluated by the Coast Guard, and their
capability has been determined to equal or exceed the response
capability needed by the vessel. For oil recovery devices, the
effective daily recovery capacity, as determined using section 6 of
this appendix, must be included. For boom, the overall boom height
(draft plus freeboard) must be included. A vessel owner or operator
must ensure that identified boom has compatible connectors.
2.8 For subparts F and G of this part, in identifying equipment,
the vessel owner or operator shall list the storage location,
quantity, and manufacturer's make and model, unless the oil spill
removal organization(s) providing the necessary response resources
have been evaluated by the Coast Guard, and their capability has
been determined to equal or exceed the response capability needed
by the vessel. For boom, the overall boom height (draft plus
freeboard) must be included. A vessel owner of operator is
responsible for ensuring that identified boom has compatible
connectors.
3. Determining Response Resources Required for the Average Most
Probable Discharge
3.1 A vessel owner or operator must identify and ensure, by
contract or other approved means, that sufficient response
resources are available to respond to the 50-barrel average most
probable discharge at the point of an oil transfer involving a
vessel that carries oil as a primary cargo or a nontank vessel
carrying oil as cargo. The equipment must be designed to function
in the operating environment at the point of oil transfer. These
resources must include -
3.1.1 Containment boom in a quantity equal to twice the length
of the largest vessel involved in the transfer capable of being
deployed within 1 hour of the detection of a spill at the site of
oil transfer operations. If the transfer operation is more than 12
miles from shore, the containment boom must be deployed within 1
hour plus the travel time from the nearest shoreline at a speed of
5 knots.
3.1.2 Oil recovery devices with an effective daily recovery
capacity of 50 barrels or greater available at the transfer site
within 2 hours of the detection of an oil discharge.
3.1.3 Oil storage capacity for recovered oily material indicated
in section 9.2 of this appendix.
4. Determining Response Resources Required for the Maximum Most
Probable Discharge
4.1 A vessel owner or operator shall identify and ensure, by
contract or other approved means, that sufficient response
resources are available to respond to discharges up to the maximum
most probable discharge volume for that vessel. The resources
should be capable of containing and collecting up to 2,500 barrels
of oil. All equipment identified must be designed to operate in the
applicable operating environment specified in table 1 of this
appendix.
4.2 To determine the maximum most probable discharge volume to
be used for planning, use the lesser of -
4.2.1 2500 barrels; or
4.2.2 Ten percent of the total oil capacity.
4.3 Oil recovery devices necessary to meet the applicable
maximum most probable discharge volume planning criteria must be
located such that they arrive on scene within 12 hours of the
discovery of a discharge in higher volume port areas and the Great
Lakes, 24 hours in all other rivers and canals, inland, nearshore,
and offshore areas, and 24 hours plus travel time from shore in all
open ocean areas.
4.3.1 Because rapid control, containment, and removal of oil is
critical to reduce spill impact, the effective daily recovery
capacity for oil recovery devices must equal 50% of the planning
volume applicable for the vessel as determined in section 4.2 of
this appendix. The effective daily recovery capacity for oil
recovery devices identified in the plan must be determined using
the criteria in section 6 of this appendix.
4.4 In addition to oil recovery capacity, the vessel owner or
operator must identify in the response plan and ensure the
availability of, through contract or other approved means,
sufficient boom available within the required response times for
oil connection and containment, and for protection of shoreline
areas. While the regulation does not set required quantities of
boom for oil collection and containment, the owner or operator of a
vessel must still identify in a response plan and ensure, through
contract or other approved means, the availability of the boom
identified in the plan for this purpose.
4.5 The plan must indicate the availability of temporary storage
capacity to meet the requirements of section 9.2 of this appendix.
If available storage capacity is insufficient to meet this
requirement, the effective daily recovery capacity must be
downgraded to the limits of the available storage capacity.
4.6 The following is an example of a maximum most probable
discharge volume planning calculation for equipment identification
in a higher volume port area:
The vessel's cargo capacity is 10,000 barrels, thus the planning
volume is 10 percent or 1,000 barrels. The effective daily recovery
capacity must be 50 percent of the planning volume, for 500 barrels
per day. The ability of oil recovery devices to meet this capacity
will be calculated using the procedures in section 6 of this
appendix. Temporary storage capacity available on scene must equal
twice the daily recovery capacity as indicated in section 9 of this
appendix, or 1000 barrels per day. This figure would represent the
information the vessel owner or operator would use to identify and
ensure the availability of, through contract or other approved
means, the required response resources. The vessel owner would also
need to identify how much boom was available for use.
5. Determining Response Resources Required for the Worst Case
Discharge to the Maximum Extent Practicable
5.1 A vessel owner or operator, as applicable under the
regulations prescribed in this part, must identify and ensure, by
contract or other approved means, that sufficient response
resources are available to respond to the worst case discharge of
oil to the maximum extent practicable. Section 7 of this appendix
describes the method to determine the required response
resources.
5.2 Oil spill recovery devices identified to meet the applicable
worst case discharge planning volume must be located such that they
can arrive at the scene of a discharge within the time specified
for the applicable response tier listed in §§ 155.1050(g) and
155.5050(g).
5.3 The effective daily recovery capacity for oil recovery
devices identified in a response plan must be determined using the
criteria in section 6 of this appendix. A vessel owner or operator,
as applicable under the regulations prescribed in this part, must
identify the storage locations of all equipment that must be used
to fulfill the requirements for each tier.
5.4 A vessel owner or operator, as applicable under the
regulations prescribed in this part, must identify the availability
of temporary storage capacity to meet the requirements of section
9.2 of this appendix. If available storage capacity is insufficient
to meet this requirement, then the effective daily recovery
capacity must be downgraded to the limits of the available storage
capacity.
5.5 When selecting response resources necessary to meet the
response plan requirements, the vessel owner or operator, as
applicable under the regulations prescribed in this part, must
ensure that a portion of those resources are capable of being used
in close-to-shore response activities in shallow water. The
following percentages of the on-water response equipment identified
for the applicable geographic area must be capable of operating in
waters of 6 feet or less depth:
(i) Open ocean - none.
(ii) Offshore - 10 percent.
(iii) Nearshore, inland, Great Lakes, and rivers and canals - 20
percent.
5.6 In addition to oil spill recovery devices and temporary
storage capacity, a vessel owner or operator, as applicable under
the regulations prescribed in this part, must identify in the
response plan and ensure the availability of, through contract or
other approved means, sufficient boom that can arrive on scene
within the required response times for oil containment and
collection. The specific quantity of boom required for collection
and containment will depend on the specific recovery equipment and
strategies employed. Table 2 of this appendix lists the minimum
quantities of additional boom required for shoreline protection
that a vessel owner or operator must identify in the response plan
and ensure the availability of, through contract or other approved
means.
5.7 A vessel owner or operator, as applicable under the
regulations prescribed in this part, must also identify in the
response plan and ensure, by contract or other approved means, the
availability of an oil spill removal organization capable of
responding to a shoreline cleanup operation involving the
calculated volume of emulsified oil that might impact the affected
shoreline. The volume of oil for which a vessel owner or operator
should plan for should be calculated through the application of
factors contained in Tables 3 and 4 of this appendix. The volume
calculated from these tables is intended to assist the vessel owner
or operator in identifying a contractor with sufficient resources.
This planning volume is not used explicitly to determine a required
amount of equipment and personnel.
6. Determining Effective Daily Recovery Capacity for Oil Recovery
Devices
6.1 Oil recovery devices identified by a vessel owner or
operator must be identified by manufacturer, model, and effective
daily recovery capacity. These capacities must be to meet the
applicable planning criteria for the average most probable
discharge; maximum most probable discharge; and worst case
discharge to the maximum extent practicable.
6.2 For the purposes of determining the effective daily recovery
capacity of oil recovery devices, the following method will be
used. This method considers potential limitations due to available
daylight, weather, sea state, and percentage of emulsified oil in
the recovered material. The Coast Guard may assign a lower
efficiency factor to equipment listed in a response plan if it
determines that such a reduction is warranted.
6.2.1 The following formula must be used to calculate the
effective daily recovery capacity:
R = T × 24 × E R - Effective daily recovery capacity T - Throughput
rate in barrels per hour (nameplate capacity) E - 20% efficiency
factor (or lower factor as determined by the Coast Guard)
6.2.2 For those devices in which the pump limits the throughput
of liquid, throughput rate will be calculated using the pump
capacity.
6.2.3 For belt or mop type devices, the throughput rate will be
calculated using data provided by the manufacturer on the nameplate
rated capacity for the device.
6.2.4 Vessel owners or operators including in the response plan
oil recovery devices whose throughput is not measurable using a
pump capacity or belt or mop capacity may provide information to
support an alternative method of calculation. This information must
be submitted following the procedures in section 6.5 of this
appendix.
6.3 As an alternative to section 6.2 of this appendix, a vessel
owner or operator may submit adequate evidence that a different
effective daily recovery capacity should be applied for a specific
oil recovery device. Adequate evidence is actual verified
performance data in spill conditions or test using certain ASTM
standards [ASTM F 631 (incorporated by reference, see § 155.140)
Standard Method for Testing Full Scale Advancing Spill Removal
Devices], or an equivalent test approved by the Coast Guard.
6.3.1 The following formula must be used to calculate the
effective daily recovery capacity under this alternative:
R = D × U R - Effective daily recovery capacity D - Average Oil
Recovery Rate in barrels per hour (Item 13.2.16 in ASTM F 631; or
actual performance data) U - Hours per day that a vessel owner or
operator can document capability to operate equipment under spill
conditions. Ten hours per day must be used unless a vessel owner or
operator can demonstrate that the recovery operation can be
sustained for longer periods.
6.4 A vessel owner or operator submitting a response plan shall
provide data that supports the effective daily recovery capacities
for the oil recovery devices listed. The following is an example of
these calculations:
A weir skimmer identified in a response plan has a
manufacturer's rated throughput at the pump of 267 gallons per
minute (gpm).
267 gpm = 381 barrels per hour R = 381 × 24 × .2 = 1,829 barrels
per day
After testing using ASTM procedures, the skimmer's oil recovery
rate is determined to be 220 gpm. The vessel owner or operator
identifies sufficient resources available to support operations 12
hours per day.
220 gpm = 314 barrels per hour R = 314 × 12 = 3,768 barrels per day
A vessel owner or operator will be able to use the higher
capacity if sufficient temporary oil storage capacity is
available.
6.5 Determinations of alternative efficiency factors under
section 6.2 or alternative effective daily recovery capacities
under section 6.3 of this appendix will be made by Commandant
(CG-MER), Attn: Vessel Response Plans, U.S. Coast Guard Stop 7516,
2703 Martin Luther King Jr. Avenue SE., Washington, DC 20593-7516
or [email protected]. Oil spill removal organizations or
equipment manufacturers may submit required information on behalf
of multiple vessel owners or operators.
7. Calculating the Worst Case Discharge Planning Volumes
7.1 A vessel owner or operator, as applicable under the
regulations prescribed in this part, must plan for a response to a
vessel's worst case discharge oil planning volume. The planning for
on-water recovery must take into account a loss of some oil to the
environment due to evaporation and natural dissipation, potential
increases in volume due to emulsification, and the potential for
deposit of some oil on the shoreline.
7.2 The following procedures must be used to calculate the
planning volume used by a vessel owner or operator, as applicable
under the regulations prescribed in this part, for determining
required on-water recovery capacity:
7.2.1 The following must be determined: the total volume of oil
cargo carried; the appropriate cargo group for the type of
petroleum oil carried [persistent (groups II, III, and IV) or
non-persistent (group I)]; and the geographic area(s) in which the
vessel operates. For vessels carrying mixed cargoes from different
petroleum oil groups, each group must be calculated separately.
This information is to be used with Table 3 of this appendix to
determine the percentages of the total cargo volume to be used for
removal capacity planning. This table divides the cargo volume into
three categories: oil lost to the environment; oil deposited on the
shoreline; and oil available for on-water recovery.
7.2.2 The on-water oil recovery volume must be adjusted using
the appropriate emulsification factor found in Table 4 of this
appendix.
7.2.3 The adjusted volume is multiplied by the on-water oil
recovery resource mobilization factor found in Table 5 of this
appendix from the appropriate operating area and response tier to
determine the total on-water oil recovery capacity in barrels per
day that must be identified or contracted for to arrive on scene
within the applicable time for each response tier. Table 5
specifies three tiers. For higher volume port areas, the contracted
tiers of resources must be located such that they can arrive on
scene within 12, 36, and 60 hours of the discovery of an oil
discharge. For the Great Lakes, these tiers are 18, 42, and 66
hours. For rivers and canals, inland, nearshore, and offshore,
these tiers are 24, 48, and 72 hours. For the open ocean area,
these tiers are 24, 48, and 72 hours with an additional travel time
allowance of 1 hour for every additional 5 nautical miles from
shore. For nontank vessels, only Tier 1 is specified.
7.2.4 The resulting on-water recovery capacity in barrels per
day for each tier is used to identify response resources necessary
to sustain operations in the applicable geographic area. The
equipment must be capable of sustaining operations for the time
period specified in Table 3 of this appendix. A vessel owner or
operator, as applicable under the regulations prescribed in this
part, must identify and ensure the availability of, through
contract or other approved means, sufficient oil spill recovery
devices to provide the effective daily oil recovery capacity
required. If the required capacity exceeds the applicable cap
described in Table 6 of this appendix, then a vessel owner or
operator must contract only for the quantity of resources required
to meet the cap, but must identify sources of additional resources
as indicated in § 155.1050(p). For a vessel that carries multiple
groups of oil, the required effective daily recovery capacity for
each group is calculated and summed before applying the cap.
7.3 The following procedures must be used to calculate the
planning volume for identifying shoreline cleanup capacity:
7.3.1 The following must be determined: The total volume of oil
carried; the appropriate group for the type of petroleum oil
carried [persistent (groups II, III, and IV) or non-persistent
(group I)]; and the geographic area(s) in which the vessel
operates. For a vessel carrying different oil groups, each group
must be calculated separately. Using this information, Table 3 of
this appendix must be used to determine the percentages of the
total oil volume to be used for shoreline cleanup resource
planning.
7.3.2 The shoreline cleanup planning volume must be adjusted to
reflect an emulsification factor using the same procedure as
described in section 7.2.2 of this appendix.
7.3.3 The resulting volume will be used to identify an oil spill
removal organization with the appropriate shoreline cleanup
capability.
7.4 The following is an example of the procedure described
above:
A vessel with a 100,000 barrel capacity for #6 oil (specific
gravity .96) will move from a higher volume port area to another
area. The vessel's route will be 70 miles from shore.
Cargo carried: 100,000 bbls. Group IV oil Emulsification factor
(from Table 4 of this appendix): 1.4 Areas transited: Inland,
Nearshore, Offshore, Open ocean Planned % on-water recovery (from
Table 3 of this appendix): Inland 50% Nearshore 50% Offshore 40%
Open ocean 20% Planned % oil onshore recovery (from Table 3 of this
appendix): Inland 70% Nearshore 70% Offshore 30% Open ocean 30%
General formula to determine planning volume: (planning volume) =
(capacity) × (% from Table 3 of this appendix) × (emulsification
factor from Table 4 of this appendix) Planning volumes for on-water
recovery: Inland 100,000 × .5 × 1.4 = 70,000 bbls Nearshore 100,000
× .5 × 1.4 = 70,000 bbls Offshore 100,000 × .4 × 1.4 = 56,000 bbls
Open ocean 100,000 × .2 × 1.4 = 28,000 bbls Planning volumes for on
shore recovery: Inland 100,000 × .7 × 1.4 = 98,000 bbls Nearshore
100,000 × .7 × 1.4 = 98,000 bbls Offshore 100,000 × .3 × 1.4 =
42,000 bbls The vessel owner or operator must contract with a
response resource capable of managing a 98,000-barrel shoreline
cleanup in those areas where the vessel comes closer than 50 miles
to shore.
Determining required resources for on-water recovery for each
tier using mobilization factors: (barrel per day on-water recovery
requirements) = (on-water planning volume as calculated above) ×
(mobilization factor from Table 5 of this appendix).
|
|
Tier 1 |
Tier 2 |
Tier 3 |
Inland/Nearshore
70,000 |
× |
.15 |
.25 |
.40 |
Offshore
56,000 |
× |
.10 |
.165 |
.21 |
Open ocean
28,000 |
× |
.06 |
.10 |
.12 |
equals (barrels per day) |
Inland/Nearshore |
|
10,500 |
17,500 |
28,000 |
Offshore |
|
5,600 |
9,240 |
11,760 |
Open ocean |
|
1,680 |
2,800 |
3,360 |
Since the requirements for Tier 1 for inland and nearshore
exceed the caps, the vessel owner would only need to contract for
10,000 barrels per day for Tier 1. No additional equipment would be
required to be identified because the required Tier 3 resources are
below the Tier 3 caps.
10% of the on-water recovery capability for offshore, and 20% of
the capability for inland/nearshore, for all tiers, must be capable
of operating in water with a depth of 6 feet or less.
The vessel owner or operator would also be required to identify
or contract for quantities of boom identified in Table 2 of this
appendix for the areas in which the vessel operates.
8. Determining the Capability of High-Rate Response Methods
8.1 Calculate cumulative dispersant application capacity
requirements as follows:
8.1.1 A vessel owner or operator, as applicable under the
regulations prescribed in this part, must plan either for a
dispersant capacity to respond to a vessel's worst case discharge
of oil, or for the amount of the dispersant resource capability as
required by § 155.1050(k)(3) of this subchapter, whichever is the
lesser amount. When planning for the cumulative application
capacity that is required, the calculations should account for the
loss of some oil to the environment due to natural dissipation
causes (primarily evaporation). The following procedure should be
used to determine the cumulative application requirements:
8.1.2 Determine the WCD volume of oil carried in gallons, and
the appropriate oil group for the type of petroleum oil carried
(Groups II, III, IV). For vessels carrying different oil groups,
assume a WCD using the oil group that constitutes the largest
portion of the oil being carried, or the oil group with the
smallest natural dissipation factor;
8.1.3 Multiply the WCD in gallons by the natural dissipation
factor for the appropriate oil group as follows: Group II factor is
0.50; Group III factor is 0.30; and Group IV factor is 0.10. This
represents the amount of oil that can be expected to be lost to
natural dissipation. Subtract the WCD lost to natural dissipation
from the total oil amount carried to determine the remaining oil
available for treatment by dispersant-application; and
8.1.4 Multiply the oil available for dispersant treatment by the
dispersant to oil planning application ratio of 1 part dispersant
to 20 parts oil (0.05). The resulting number represents the
cumulative total dispersant-application capability that must be
ensured available within the first 60 hours.
8.1.5(i) The following is an example of the procedure described
in paragraphs 8.1.1 through 8.1.4 above: A vessel with a 1,000,000
gallons capacity of crude oil (specific gravity 0.87) will transit
through an area with pre-authorization for dispersant use in the
nearshore environment on the U.S. East Coast.
WCD: 1,000,000 gallons, Group III oil.
Natural Dissipation Factor for Group III: 30 percent.
General formula to determine oil available for dispersant
treatment: ((WCD) - [(WCD) × (natural dissipation factor)] =
available oil.
E.g., 1,000,000 gal−(1,000,000 gal × 0.30) = 700,000 gallons of
available oil.
Cumulative application capacity = Available oil × planning
application ratio (1 gal dispersant/20 gals oil = 0.05).
E.g., 700,000 gal oil × (0.05) = 35,000 gallons cumulative
dispersant-application capacity.
(ii) The requirements for cumulative dispersant-application
capacity (35,000) for this vessel's WCD is less than the overall
dispersant capability cap for non-Gulf Coast waters required by §
155.1050(k) of this chapter. Because paragraph 8.1.1 of this
appendix requires owners and operators to ensure the availability
of the lesser of a vessel's dispersant requirements for WCD or the
amount of the dispersant cap provided for in § 155.1050(k)(3), the
vessel in this example would be required to ensure the availability
of 35,000 gallons of dispersant. More specifically, this vessel
would be required to meet the following tier requirements in §
155.1050(k), which total 35,000 gallons application:
Tier - 1 4,125 gallons - Completed in 12 hours.
Tier - 2 23,375 gallons - Completed in 36 hours.
Tier - 3 7,500 gallons - Completed in 60 hours.
8.2 Determining Effective Daily Application Capacities “EDACs”
for dispersant response systems as follows:
8.2.1 EDAC planning estimates for compliance with the dispersant
application requirements in § 155.1050(k)(3) are to be based
on:
8.2.1.1 The spill occurring at sites 50 nautical miles off shore
furthest from the primary dispersant staging site(s);
8.2.1.2 Specific dispersant application platform operational
characteristics identified in the EDSP or as demonstrated by
operational tests;
8.2.1.3 Locations of primary dispersant staging sites; and
8.2.1.4 Locations and quantities of dispersant stockpiles.
8.2.2 EDAC calculations with supporting documentation must be
submitted to the NSFCC for classification as a Dispersant Oil Spill
Removal Organization.
8.2.3(i) EDAC can also be calculated using the EDSP (EDSP). The
EDSP is a downloadable application that calculates EDAC for
different dispersant response systems. It is located on the
Internet at:
http://www.response.restoration.noaa.gov/spilltools
(ii) The DMP2 contains operating information for the vast
majority of dispersant application platforms, to include aircraft,
both rotary and fixed wing, and vessels. The DMP2 produces EDAC
estimates by performing calculations that are based on performance
parameters of dispersant application platforms, locations of
primary dispersant staging sites, home based airport or port
locations, and for planning purposes, a 50 mile from shore
dispersant application site. The 50 mile offshore site used in the
DMP2 would be the location furthest from the primary dispersant
staging site identified in the vessel response plan.
8.2.4 For each Captain of the Port Zone where a dispersant
response capability is required, the response plan must identify
the following:
8.2.4.1 The type, number, and location of each dispersant
application platform intended for use in meeting dispersant
delivery requirements specified in § 155.1050(k)(3) of this
chapter;
8.2.4.2 The amount and location of available dispersant
stockpiles to support each platform; and
8.2.4.3 A primary staging site for each platform that will serve
as its base of operations for the duration of the response.
8.3 In addition to the equipment and supplies required, a vessel
owner or operator must identify a source of support to conduct the
monitoring and post-use effectiveness evaluation required by
applicable Local and Area Contingency Plans.
8.4 Identification of the resources for dispersant application
does not imply that the use of this technique will be authorized.
Actual authorization for use during a spill response will be
governed by the provisions of the National Oil and Hazardous
Substances Contingency Plan (40 CFR part 300) and the applicable
Local or Area Contingency Plan.
9. Additional Equipment Necessary To Sustain Response Operations
9.1 A vessel owner or operator is responsible for ensuring that
sufficient numbers of trained personnel, boats, aerial spotting
aircraft, sorbent materials, boom anchoring materials, and other
resources are available to sustain response operations to
completion. All such equipment must be suitable for use with the
primary equipment identified in the response plan. A vessel owner
or operator is not required to list these resources in the response
plan, but shall certify their availability.
9.2 A vessel owner or operator shall evaluate the availability
of adequate temporary storage capacity to sustain the effective
daily recovery capacities from equipment identified in the plan.
Because of the inefficiencies of oil spill recovery devices,
response plans must identify daily storage capacity equivalent to
twice the effective daily recovery capacity required on scene. This
temporary storage capacity may be reduced if a vessel owner or
operator can demonstrate by waste stream analysis that the
efficiencies of the oil recovery devices, ability to decant water,
or the availability of alternative temporary storage or disposal
locations in the area(s) the vessel will operate will reduce the
overall volume of oily material storage requirements.
9.3 A vessel owner or operator shall ensure that their planning
includes the capability to arrange for disposal of recovered oil
products. Specific disposal procedures will be addressed in the
applicable Area Contingency Plan.
Table 1 - Response Resource Operating
Criteria
[Oil Recovery Devices]
Operating
Environment |
Significant Wave Height
1 |
Sea State |
(feet) |
Rivers &
Canals |
≤1 |
1 |
Inland |
≤3 |
2 |
Great Lakes |
≤4 |
2-3 |
Ocean |
≤6 |
3-4 |
Boom
Property |
Use |
Rivers & Canals |
Inland |
Great Lakes |
Ocean |
Significant Wave
1 2 Height (feet) |
≤1 |
≤3 |
≤4 |
≤6 |
Sea State |
1 |
2 |
2-3 |
3-4 |
Boom height -
in. |
6-18 |
18-42 |
18-42 |
≥42 |
(draft plus
freeboard) |
|
|
|
|
Reserve Buoyancy
to Weight Ratio |
2:1 |
2:1 |
2:1 |
3:1 to 4:1 |
Total Tensile
Strength - lbs. |
4,500 |
15-20,000 |
15-20,000 |
>20,000 |
Skirt Fabric
Tensile Strength - lbs. |
200 |
300 |
300 |
500 |
Skirt Fabric Tear
Strength - lbs. |
100 |
100 |
100 |
125 |
Table 2 - Shoreline Protection
Requirements
Location |
Boom |
Availability
hours |
Ensured by contract or other
approved means (ft.) |
Higher volume port area |
Other areas |
Persistent Oils |
Open Ocean |
|
|
|
Offshore |
15,000 |
24 |
48 |
Nearshore/Inland/Great Lakes |
30,000 |
12 |
24 |
Rivers &
Canals |
25,000 |
12 |
24 |
Non-Persistent Oils |
Open Ocean |
|
|
|
Offshore |
|
|
|
Nearshore/Inland/Great Lakes |
10,000 |
12 |
24 |
Rivers &
Canals |
15,000 |
12 |
24 |
Table 4 - Emulsification Factors for
Petroleum Oil Cargo Groups
Non-persistent oil
72 G: |
|
Group I |
1.0 |
Persistent
oil: |
|
Group II |
1.8 |
Group III |
2.0 |
Group IV |
1.4 |
Table 5 - On-Water Oil Recovery Resource
Mobilization Factors
Area |
Tier 1 |
Tier 2 |
Tier 3 |
Rivers and
Canals |
.30 |
.40 |
.60 |
Inland/Nearshore/Great Lakes |
.15 |
.25 |
.40 |
Offshore |
.10 |
.165 |
.21 |
Ocean |
.06 |
.10 |
.12 |
Table 6 - Response Capability Caps by
Geographic Area
|
Tier 1 |
Tier 2 |
Tier 3 |
As of February 18,
1993: |
|
|
|
All except rivers
& canals & Great Lakes |
10K bbls/day |
20K bbls/day |
40K bbls/day. |
Great Lakes |
5K bbls/day |
10K bbls/day |
20K bbls/day. |
Rivers &
canals |
1,500 bbls/day |
3,000 bbls/day |
6,000 bbls/day. |
February 18,
1998: |
|
|
|
All except rivers
& canals & Great Lakes |
12.5K bbls/day |
25K bbls/day |
50K bbls/day. |
Great Lakes |
6.35K bbls/day |
12.5K bbls/day |
25K bbls/day. |
Rivers &
canals |
1,875 bbls/day |
3,750 bbls/day |
7,500 bbls/day. |
February 18,
2003 |
|
|
|
All except rivers
& canals & Great Lakes |
12.5K bbls/day |
25K bbls/day |
50K bbls/day. |
Great Lakes |
6.25K bbls/day |
12.3K bbls/day |
25K bbls/day. |
Rivers &
canals |
1,875 bbls/day |
3,750 bbls/day |
7,500 bbls/day. |
[CGD 91-034, 61 FR 1100, Jan. 12, 1996, as amended by CGD 96-026,
61 FR 33666, June 28, 1996; USCG-1999-5151, 64 FR 67176, Dec. 1,
1999; USCG-2005-21531, 70 FR 36349, June 23, 2005; USCG-2008-0179,
73 FR 35015, June 19, 2008; USCG-2001-8661, 74 FR 45029, Aug. 31,
2009; USCG-2010-0351, 75 FR 36285, June 25, 2010; USCG-2008-1070,
78 FR 60134, Sept. 30, 2013; USCG-2014-0410, 79 FR 38437, July 7,
2014; USCG-2016-0498, 82 FR 35083, July 28, 2017; USCG-2018-0874,
84 FR 30880, June 28, 2019]