C. Residential, commercial, industrial, and
recreational structures
1. Policies
a. It shall be the policy of the Council to
undertake all appropriate actions to prevent, minimize or mitigate the risks of
storm damage to property and coastal resources, endangerment of lives and the
public burden of post storm disaster assistance consistent with policies of the
State of Rhode Island as contained in the Hazard Mitigation Plan element of the
State Guide Plan when considering applications for the construction of
residential, commercial, industrial and recreational structures, including
utilities such as gas, water and sewer lines, in high hazard areas.
b. It is the Council's policy to require a
public access plan, in accordance with § 1.3.6 of this Part, as part of
any application for a commercial or industrial development or redevelopment
project in or impacting coastal resources. In accordance with § 1.1.7 of
this Part, a variance from this policy may be granted if an applicant can
demonstrate that no significant public access impacts will occur as result of
the proposed project.
c. All
commercial and industrial structures and operations located within tidal waters
shall obtain a structural perimeter limit (SPL). Owners/operators of these
facilities may apply to the Council for definition and establishment of this
structural perimeter at any time. However, the Council shall establish a
structural perimeter limit (SPL) when an application subject to this section is
under review.
2.
Prerequisites
a. Applicants proposing new
construction and/or alterations to existing structures shall obtain a letter
from the local authorities certifying that proposed activities conform to the
local zoning ordinance, or that if relief from an ordinance is required that it
has been obtained and that the decision authorizing the appropriate relief is
final. This letter must be submitted to the CRMC with the application.
b. Applicants proposing new
construction and/or alterations to existing structures shall demonstrate that
all applicable requirements of the RI state building code (SBC) including those
pertaining to construction within flood hazard zones will be met. This
demonstration shall be made by submitting to the CRMC at the time of
application a building official's form properly completed and signed by the
local building official.
c.
Applicants proposing to build, repair or alter an onsite wastewater treatment
system (OWTS) shall obtain a permit from the Department of Environmental
Management and shall submit to the CRMC copies of the approved application and
the approved plans. The plan submitted must bear a DEM/OWTS approval
stamp.
d. Persons proposing
activities that may impact the function of an existing OWTS and which by the
rules and regulations of the Department of Environmental Management requires
the issuance of a permit, shall obtain the necessary permits and submit copies
of these permits to the CRMC at the time of application.
e. Applicants for industrial, commercial and
recreational structures shall demonstrate that all state safety codes, fire
codes, and environmental requirements have or will be met.
f. Applicants shall demonstrate that
connections to public water supplies and sewer systems shall be authorized by
the appropriate authorities when:
(1) Such
connections are proposed by the applicant; or
(2) Where on-site water withdrawal and/or
sewage disposal will have a significant adverse environmental or public health
impact.
g. Applicants
for commercial, industrial, and recreational structures shall demonstrate that
adequate transportation and utility services to support the proposed operations
and related activities are available.
3. Prohibitions
a. Industrial operations and structures are
prohibited in Type 1 and 2 waters or on shoreline features abutting these
waters.
b. The mining and
extraction of minerals, including sand and gravel, from tidal waters and salt
ponds is prohibited. This prohibition does not apply to dredging for navigation
purposes, channel maintenance, habitat restoration, or beach
replenishment.
c. Solid waste
disposal and minerals extraction is prohibited on shoreline features and their
contiguous areas.
d. The use of
fill for structural support of buildings in flood hazard V zones is
prohibited.
e. New decks and
structures, and expanded structures associated with residential properties, or
non-water dependent commercial uses, are prohibited in or over tidal
waters.
f. Decks associated with
commercial properties are prohibited in or over type 1 waters. Decks associated
with commercial properties are prohibited in or over Type 2 waters unless such
use is reserved in connection with a water dependent use. Decks associated with
commercial properties are prohibited in or over Type 3, 4, 5, and 6 waters
unless:
(1) The deck is to accommodate a
designated priority use for that water area;
(2) The applicant has examined all reasonable
alternatives and the council has determined that the selected alternative is
the most reasonable; and
(3) The
deck is the minimum necessary to support the priority use.
g. See Table 2 in § 1.1.4 of this Part
for a listing of additional prohibitions.
4. Standards
a. General:
(1) See standards given in "Filling,
Removing, or Grading of Shoreline Features" in §1.3.1(B) of this Part, as
applicable.
(2) See standards given
in "Sewage Treatment and Disposal" in §1.3.1(F) of this Part, as
applicable.
(3) Commercial and
Industrial docks, wharves and piers shall be designed and certified by a
registered professional engineer.
(4) All commercial and industrial structures
and operations in tidal waters shall have a defined structural perimeter for
in-water facilities, which shall describe and limit that area in which repair
or alteration activities may take place. Structural perimeters shall be defined
on the basis of in-water facilities in place as of September 30, 1971, or
subsequently assented structures. All new or modified structural perimeter
limit lines shall be a maximum of ten (10) feet outside of the structures. The
structural perimeter limit (SPL) shall be designated on all plans with the
corners designated by their State Plane Coordinates. However, in all cases the
SPL shall be setback at least fifty (50) feet from approved mooring fields. In
addition the SPL shall be setback at least three times the authorized project
depth from federal navigation projects (e.g. navigation channels and anchorage
areas).
(5) It is permissible to
have vessels berthed at a facility outside of the structural perimeter limit
if, in the opinion of the Executive Director, there are no conflicts with other
users, impacts to resources, or conflicts with the DEM Shellfish Program. All
vessels shall be berthed parallel to piers and docks if outside of the
structural perimeter limit.
b. All new or existing commercial marine
facilities (CMF) as defined in § 1.1.2 of this Part shall perform fitness
of purpose inspections in accordance with the CRMC "Guidelines for Fitness of
Purpose Investigations and Certifications." The addition of new structural
components or systems on existing CMFs that are structurally independent of the
existing components or systems shall be considered as "new."
(1) A post-event inspection is required for
any CMF following a significant potentially damage-causing event such as a
hurricane, vessel impact, fire or explosion. The primary purpose is to assess
the integrity of structural and mechanical systems. This assessment will
determine the operational status and/or any remedial measures required by the
CRMC for the CMF.
(2) Post event
notification shall be provided to the CRMC. The notification shall include, as
a minimum:
(AA) Brief description of the
event;
(BB) Brief description of
the nature, extent and significance of any damage observed as a result of the
event;
(CC) Operational status and
any required restrictions; and
(DD)
Statement as to whether a post-event inspection will be carried-out.
(3) The CRMC may carry out or
cause to be carried out, a post-event inspection. In the interim, the CRMC may
modify or limit the operations through Assent suspension. If a post-event
inspection is required, an action plan shall be submitted to the CRMC within
five (5) days after the event. This deadline may be extended in special
circumstances. The action plan shall include the scope of the inspection (above
water, underwater, mechanical systems, physical limits, applicable berthing
systems, etc.) and submission date of the final report. The action plan is
subject to CRMC approval.
c. Residential, commercial, industrial, and
recreational buildings:
(1) Excavation and
grading shall be restricted to those activities and areas necessary for the
construction of the building and/or appurtenant structures (see §1.3.1(B)
of this Part).
(2) Applicants shall
be required to reduce the inflow of pollutants carried by surface runoff in
accordance with the policies and standards contained in §1.3.1(F) of this
Part and as detailed in the most recent version of the Rhode Island Stormwater
Design and Installation Standards Manual.
6. Flood zone construction. In many instances
lands under the jurisdiction of the CRMC are by virtue of their topographic
position subject to flooding. The Federal Emergency Management Agency has
evaluated the risk of flooding and has established one hundred (100) year
return frequency elevations of the flood waters (i.e., the Base Flood
Elevation, (BFE) for all of the State's coastal communities. The approximate
limits of the flood zones and the associated Base Flood Elevations are shown on
the FEMA Flood Insurance Rate Maps, which are commonly available at each
communities building official's office. In recognition that structures located
within Flood Hazard Zones must be designed to meet more severe conditions than
those not, the Rhode Island State Building Code, (RISBC) contains specific
requirements for flood zone construction.
a.
The CRMC requires all applicants proposing construction within flood hazard
zones to demonstrate that all applicable portions of the RISBC are to be met.
This demonstration shall be made by submitting to the CRMC at the time of
application a building official's form properly completed and signed by the
local building official.
7. Construction in flood hazard zones. In
addition to the requirements of the RISBC, the CRMC suggests that applicants
incorporate the following items into their proposed designs:
a. For construction in wave velocity (V)
zones as defined by FEMA Flood Insurance Rate Maps:
(1) If timber pilings are used, they should
meet the American Society for Testing and Materials (ASTM) standards for Class
B piles and shall have a minimum tip diameter of 8 inches. Wooden pilings
should be treated with a wood preservative. Bracing between piles is
recommended.
(2) Pilings in ocean
fronting areas should penetrate no less than ten (10) feet below mean sea
level.
(3) Floor joists should be
secured with hurricane clips where each joist encounters a floor beam. These
metal fasteners or straps should be nailed on the joist as well as on the
beam.
(4) To secure the exterior
wall to the floor joists, galvanized metal strap connections should be used
connecting the exterior wall studs to the joists.
(5) Roof trusses or rafters should be
connected to the exterior wall with galvanized metal straps.
b. For construction in coastal (A)
Flood Zones.
(1) Items 1, 2, 3, 4, 5 as listed
in §1.3.1(C)(7)(a) of this Part for V zone construction should, if
applicable, be employed.
(2)
Parallel concrete walls or pilings rather than fill should be used to elevate
habitable residential structures when six (6) feet or more clearance exists
between the existing grade and the flood plain elevation.
(3) In areas subject to minimal wave action
in a one hundred (100) year storm event, discontinuous reinforced concrete
foundation walls which allow sufficient free flow of flood waters may be
substituted for parallel concrete walls or pilings.
D. Recreational boating
facilities
1. Policies
a. Pursuant to R.I. Gen. Laws §
46-23-6(9)
recreational boating facilities as defined in § 1.1.2 of this Part by and
properly permitted by the Council, are deemed to be one of the uses consistent
with the public trust.
c. The
Council recognizes that the United States Coast Guard has primary authority
over navigational aids and marine boating safety, and that these
responsibilities are complemented by the Department of Environmental
Management, local harbormasters, and public boating service organizations such
as the Coast Guard Auxiliary.
d.
The Council requires municipalities preparing to implement harbor management
plans and/or programs relating to activities in tidal waters to apply for a
determination of consistency with the Coastal Resources Management Program to
assure conformance between such plans and/or programs and the Coastal Resources
Management Program, the Guidelines for the Development of Municipal Harbor
Management Plans and the General Laws of the State of Rhode Island.
e. All persons proposing condominium,
dockominium, or other forms of ownership or operation of recreational boating
facilities involving multiple, cooperative, condominium or fee simple interests
in ownership or operation shall submit a prospectus of such proposals to the
CRMC for review of consistency with the state of Rhode Island's public trust
responsibilities, R.I. Gen. Laws Chapter 46-23, and the Rhode Island Coastal
Resources Management Program.
f.
Repair or reconstruction of all residential structures that are physically
destroyed fifty percent (50%) or more by wind, storm surge, waves or other
coastal processes shall require a new Council assent. Such activities requiring
a new Council assent shall be reviewed according to the most current applicable
programmatic requirements of the Coastal Resources Management Program, its
Special Area Management Plans, and/or any other appropriate CRMC-approved
management plan. All replacement structures shall be designed and constructed
to meet current structural and environmental design conditions shown in Table 8
of this Part (Minimum design criteria). For marinas see §1.3.1(N) of this
Part.
g. Table 6: Existing
residential and limited recreational boating facility modification request for
permitted structures
Dock condition
|
Application type
|
Functional dock to be replaced in its
entirety
|
Maintenance
|
Functional dock to be replaced in its entirety in
Type 1 waters
|
Maintenance
|
Functional Dock destroyed (>50%) by storm or
natural Hazard in Type 1 Waters
|
Cannot be replaced or special Exception
|
Existing Dock field assessed by CRMC Staff as
>50% destroyed in Type 1 Waters
|
Cannot be Replaced or Special Exception
|
Functional Dock, destroyed (>50%) in a
storm/natural hazard
|
New
|
Dock, not functional, field assessed as >50%
destroyed
|
New
|
Functional Dock, to be replaced in its
entirety
|
Refer to §1.3.1(N) of this Part
|
dock, not in compliance at time of permit
|
Refer to §1.3.1(N) of this Part
|
Adding to existing Dock
|
Existing dock does not need to be brought into
compliance; proposed addition must meet current regulations
|
Modification
|
Addition is over fifty percent (50%) of length or
width of dock
|
New
|
h.
In the event of catastrophic storms, § 1.1.12 of this Part (Emergency
Assents) may apply to the above table at the discretion of the Executive
Director.
i. Outhauls are subject
to the regulatory jurisdiction of the Council. The Council may authorize a
municipality to administer an annual permit for such provided said municipality
has a Council approved and active harbor management plan and ordinance which
contains the following municipal documentation that demonstrates that:
(1) Except as provided below, an outhaul(s)
is/are to be permitted to the contiguous waterfront property owner;
and,
(2) Up to two (2) outhauls may
be allowed per waterfront property; and,
(3) Outhauls are not permitted on properties
which contain a recreational boating facility; and,
(4) Procedures have been adopted to ensure
that permits are only issued consistent with the RICRMP, including the
provisions of §1.3.1(R) of this Part; and,
(5) The procedures acknowledge that the CRMC
retains the authority to revoke any permits issued by the municipality if it
finds that such permit conflicts with the RICRMP; and,
(6) From November 15 to April 15, when a boat
is not being secured by the device on an annual basis, the outhaul cabling
system shall be removed; and,
(7)
Outhauls may be "grandfathered" in their current location upon annual
harbormaster documentation that such outhauls have been in continuous use at
such location since 2004, and, the contiguous property owner(s) agree in
writing to such, however, such "grandfathering" is extinguished whenever a
recreational boating facility is approved at the location.
j. The Council may recognize and issue its
own Assent for a preexisting recreational boating facility upon proof of an
Army Corps of Engineers permit; a town or city council authorization issued
prior to 1972; a harbor commission authorization issued prior to 1972; and/or,
a Rhode Island Division of Harbors and Rivers permit issued prior to 1972. The
CRMC will issue a registration plate and number that will be assigned to that
specific structure.
2.
Marina policies
a. The Council encourages
marinas to utilize techniques that make the most efficient use of space and
increased demands for moorage, dockage, and storage space by primarily
utilizing dry stack storage in addition to innovative slip and mooring
configurations, etc.
b. All new and
significantly expanded marinas shall first submit a preliminary determination
(PD) application to the CRMC for a conceptual evaluation of the proposed
project. The preliminary determination shall include an alternatives analysis
to evaluate that the use of the public trust resources proposed are the most
efficient and protective of the environment. The primary objective of the PD
shall be to document all efforts to avoid adverse impacts and to minimize and
offset unavoidable adverse impacts to aquatic and terrestrial resources. Such
documentation shall be in the form of an objective analysis of alternatives
that satisfies the above review criteria and provides an evaluation of
practicable alternate sites and/or designs. The applicant shall be required to
attend a meeting with the CRMC staff to review the results of the preliminary
determination. In assessing a proposed marina facility, the Council shall
require a preliminary determination/alternatives analysis that details the
following:
(1) The appropriateness of the
facility given the activities potential to impact Rhode Island's coastal
resources;
(2) The appropriateness
of the structure given environmental site conditions;
(3) The potential impacts of the structure
and use of the facility on public trust resources (e.g., fin fish, shellfish,
submerged aquatic vegetation, benthic habitat, commerce, navigation,
recreation, natural resources, and other uses of the submerged lands,
etc.);
(4) The potential navigation
impacts of the structure and associated use of the structure;
(5) The potential aesthetic and scenic
impacts associated with the structure;
(6) The cumulative impacts associated with
the increased density of existing recreational boating facilities in the
vicinity of the proposed project. In considering these factors, the Council
shall weigh the benefits of the proposed activity against its potential impacts
while ensuring that it does not cause an adverse impact on other existing uses
of Rhode Island's public trust resources;
(7) The potential impacts to other
recreational or commercial uses of the affected resource;
(8) The extent to which any disruption of the
public use of such lands is temporary or permanent;
(9) The extent to which the public at large
would benefit from the activity or project and the extent to which it would
suffer detriment; and
(10) The
extent to which structures that extend over submerged lands are dependent upon
water access for their primary purpose.
c. It is the policy of the Council that the
applicant demonstrates through measurable standards referred to herein that the
marina expansion cannot be accomplished within the existing Marina Perimeter
Limit through utilization of more efficient configurations.
d. The Council shall require persons
proposing to construct new marina facilities or proposing to expand existing
marina facilities to undertake measures that mitigate the adverse impacts to
water quality associated with the proposed activity. Applicants shall apply for
a Water Quality Certificate from the RI Department of Environmental Management
and Army Corps of Engineers Permit, concurrent with their application to
CRMC.
e. The construction of
marinas, docks, piers, floats and other recreational boating facilities located
on tidal lands or waters constitutes a use of Rhode Island's public trust
resources. Due to the CRMC's legislative mandate to manage Rhode Island's
public trust resources for this and subsequent generations, the Council must
assess all proposed uses of public trust lands or waters on a case-by-case
basis, examine reasonable alternatives to the proposed activity, and ensure
that the public's interests in the public trust resources are
protected.
f. It is the Council's
policy that new or significant marina expansions must demonstrate:
(1) There is no alternative within the
current in-water perimeter that would accommodate the expansion;
(2) The area requested is the minimum
necessary; and
(3) The request
avoids or minimizes impact to the aquatic environment and traditional uses in
the area.
g. The Council
encourages all recreational boating facilities to provide an opportunity for a
variety of boat sizes and types so as to provide access for the widest segment
of the public to the Public Trust Resources.
h. It is the Council's policy to require a
public access plan or an enhancement to existing access, in accordance with
§ 1.3.6 of this Part (Protection & Enhancement of Public Access to the
Shore), as part of any application for a new marina, or for a significant
expansion to any existing marina. In accordance with § 1.1.7 of this Part,
a variance from this policy may be granted if an applicant can demonstrate that
no significant adverse public access impacts will occur as a result of the
project. The public access plan must detail the vehicle parking that will be
provided to support the proposed public access. All boating facilities shall be
designed and constructed in a manner which does not impede or detract from and
whenever practicable promote public access along and to the shore.
3. Residential and limited
recreational boating facility policies
a. All
residential and limited recreational boating facilities are required to be
registered by and with the Council and have posted on them a registration plate
and number issued by the Council. The registration plate and number must be
permanently affixed to the facility on its most seaward face and be visible
from the navigation channel or fairway to the structure at all times.
b. In order to limit the cumulative impacts
of multiple individual residential and limited recreational boating facilities,
the Council encourages the construction of facilities that service a number of
users. It is the policy of the Council to manage the siting and construction of
recreational and limited recreational boating facilities within the public
tidal waters of the state to prevent congestion, and with due regard for the
capability of coastal areas to support boating and the degree of compatibility
with other existing uses of the state's waters and ecological
considerations.
c. All recreational
and limited recreational boating facilities shall be designed and constructed
to adequately withstand appropriate environmental conditions present at the
site and to minimize impacts to existing resources.
d. All residential boating facilities shall
be contiguous to a private residence, condominium, cooperative or other
homeowner's association property and shall not accommodate more than four (4)
boats.
e. All limited recreational
boating facilities must be contiguous to property zoned by the local
municipality as institutional or open space (or an appropriate sub-district of
institutional or open space zoning) and shall not accommodate more than four
(4) boats.
f. It is the Council's
policy to authorize only one (1) residential or limited recreational boating
facility per lot of record as of October 7, 2012 to minimize user conflicts and
cumulative impacts in tidal waters.
g. Assents for limited recreational boating
facilities remain valid provided the local parcel zoning remains unchanged from
the time of the Assent. Modification of the local zoning designation to a
category other than open space or institutional or their appropriate
sub-district categories automatically nullifies the CRMC Assent.
h. It is the Council's policy to ultimately
remove all recreational boating facilities located in Type 1 waters (see
§1.2.1(A) of this Part). The Council recognizes that pre-existing
recreational boating facilities in Type 1 waters built prior to January 1, 1985
may not meet current Council standards and policies. Such facilities are not
required to reapply under this subsection provided the Council has authorized
the facility by issuance of an assent including maintenance. Unless such
facilities have been previously authorized by the Council, such facilities
shall not pose any significant risk to the coastal resources of the state, such
as significant impacts to salt marshes, and shall not endanger human safety to
be eligible for an assent. Applicants shall provide clear and convincing
evidence for unauthorized preexisting recreational boating facilities that:
(1) The facility exists in substantially the
same configuration as it did prior to January 1, 1985;
(2) The facility is presently intact and
functional; and
(3) The facility
presents no significant threat to coastal resources nor to human
safety.
4.
Prerequisites
a. All new or significantly
expanded recreational and limited recreational boating facilities shall be
within the property line extensions of the proposed facility or have a signed
agreement with the adjacent land owner(s) whose property line extension area is
impacted. All structures shall be a minimum of twenty-five (25) feet from the
property line extension. Otherwise the applicant shall have a letter of no
objection from the adjacent property owner stating that the reduced setback is
acceptable. This letter and variance request shall be provided with the
application.
5. Marina
prerequisites
a. Persons proposing to
establish a new marina or significantly expand a marina shall prepare and
submit a preliminary determination application prior to submitting a Category B
application.
b. If in the opinion of
the Council or executive director the proposed marina or significant expansion
is not utilizing the public trust in accordance with this Section the applicant
may be required to prepare alternative layouts that meet the standards
herein.
c. The preliminary
determination for new or significant expansions of marinas must assess the
impacts of all the environmental site conditions and the planning / design
requirements below:
(1) All designs that
include water-based vessel storage are encouraged to explore both wet and dry
storage alternatives
(2) Persons
proposing to establish a new marina or significantly expand an existing marina
will be required to concurrently obtain a permit from the Army Corps of
Engineers as well as a Water Quality Certificate from the RIDEM.
(3) Persons proposing to establish a
commercial mooring area are required to concurrently obtain a permit from the
Army Corps of Engineers.
(4) An
application for a Council Assent for a marina and/or mooring area shall include
a map prepared and stamped by a professional land surveyor that designates the
area of tidal water that will be incorporated within the marina by State Plane
Coordinates (NAD83) and described by metes and bounds. All structural elements
and components shall be designed and stamped by a professional
engineer.
6.
Residential and limited recreational boating facility prerequisites:
a. All applications for residential and
limited recreational boating facilities shall be initially reviewed by the
executive director or the deputy director. The executive director or the deputy
director may refer any such application to the Council for a hearing if based
upon the application on its face a determination is made that the proposed
activity warrants a Council hearing.
b. The executive director or the deputy
director shall, based upon the application and staff reports, make a
determination that the application meets all the criteria as set out in
§1.3.1(D)(11) of this Part (standards for residential and limited
recreational docks, piers and floats) and any other applicable Council policy
or procedures. If a determination is made that all the above criteria are met,
the application shall be processed as a Category A application.
c. If a determination is made that all of the
above criteria are not met for a residential or limited recreational boating
facility then the matter shall be referred to Council as a Category B
application.
d. The executive
director or the deputy director shall have the authority to consider and act
upon variance requests to certain standards of this section pertaining to
residential and limited recreational boating facilities and shall utilize the
criteria and requirements of § 1.1.7 of this Part in its evaluation of
variance requests.
e. Variance
requests to other standards of this section or to other appropriate and
relevant sections of the CRMP must be made to the full Council. Variances shall
not be considered by the executive director or the deputy director if there is
a substantive objection, in accordance with § 1.1.6 of this Part, to the
application.
f. Variances may be
granted to all of the standards contained in §§1.3.1(D)(11) and
1.2.1(B) of this Part provided engineering, biological and other appropriate
concerns have been addressed except for the following:
(1) The executive director or the deputy
director may not grant a variance to §1.3.1(D)(11)(k) of this
Part;
(2) The executive director or
the deputy director may only grant a variance to within eighteen (18) inches of
the marsh grade standard (§1.3.1(D)(11)(g) of this Part) provided
engineering, biological, and other appropriate concerns are met; and
(3) The executive director or the deputy
director may only grant a variance for the extension of a recreational or
limited recreational boating facility out to seventy-five (75) feet beyond MLW
or up to a fifty percent (50%) increase beyond the fifty (50) foot standard
(§1.3.1(D)(11)(l) of this Part) provided engineering, biological, and
other appropriate concerns are met.
7. Prohibitions
a. The building of new marinas in Type 1 and
2 waters is prohibited.
b. The
building of recreational boating facilities in Type 1 waters is prohibited.
This prohibition shall not apply to functional structures previously authorized
by the Army Corps of Engineers, or the CRMC or predecessor agencies.
Additionally, in those instances where an applicant cannot produce an
authorization from said agencies or an approval by the Council to maintain
facilities not previously registered with the Council, but can demonstrate by
clear and convincing evidence that a recreational boating facility in Type 1
waters pre-existed and has been continuously functional prior to the formation
of the Council, the Council may grant a permit provided the applicant can meet
the requirements herein. Any assent granted pursuant to this section shall be
recorded in the land evidence records and is transferable to a subsequent owner
or purchaser of the subject property, provided however, that all assent
conditions are adhered to and the dock is removed at the termination of
assent.
c. The unloading of catches
by commercial fishing vessels at residential and limited recreational boating
facilities is prohibited.
d. The
building of structures in addition to the piles/ pile cap / stringer / deck /
handrail on a residential or limited recreational boating facility, including
but not limited to gazebos, launching ramps, wave fences, boat houses, and
storage sheds, is prohibited. However, the construction of boat lifts may be
allowed in Type 3, 5, and 6 waters, and in Type 2 waters in accordance with the
provisions of §1.3.1(P) of this Part (Boat Lift and Float Lift
Systems).
e. Rhode Island is an EPA
designated a No Discharge State; all vessel discharges within State Waters are
prohibited.
f. In Type 2 waters,
the building of private launching ramps that propose to alter a coastal feature
are prohibited, except along manmade shorelines. Where a coastal wetland fronts
a manmade shoreline, the building of private launching ramps shall be
prohibited. This prohibition does not apply to marinas with Council-approved
marina perimeters (MPL).
g. New
residential or limited recreational boating facilities are prohibited from
having both a fixed T-section or L-section, and a float.
h. Terminal Floats at residential and limited
recreational docks in excess of two hundred (200) square feet are
prohibited.
i. Residential
recreational docks shared by owners of waterfront property are prohibited from
exceeding more than two (2) terminal floats and a combined total terminal float
area in excess of three hundred (300) square feet.
j. Marine railway systems are prohibited
except in association with: a marina; or, a commercial or industrial water
dependent activity in type 3, 5 and 6 waters.
k. The installation or use of more than one
(1) residential or limited recreational boating facility per lot of record as
of October 7, 2012 is prohibited.
l. The construction and use of cribs for
residential or limited recreational boating facilities is prohibited when
located within coastal wetlands.
8. Standards
a. All new or significantly expanded
recreational boating facilities shall be located on site plans that clearly
show the mean low water (MLW) and mean high water elevation (MHW) contours. The
MLW shall be determined utilizing the "Short Term Tide Measurement" method. The
executive director shall have the discretion to require a more accurate method
of MLW determination when utilizing the Short-Term Tide Measurement method will
not provide accurate results. Guidance for the Short-Term Tide Measurement is
available from the CRMC. At the discretion of the executive director, a
previously established tidal determination may be utilized if the areas have
similar tidal characteristics.
b.
All new marinas, docks, piers, bulkheads or any other structure proposed in
tidal waters shall be designed and stamped by a registered professional
engineer licensed in the State of Rhode Island.
c. All structural elements shall be designed
in accordance with Minimum Design Criteria or the Minimum Design Loads for
Buildings and Other Structures, current Edition published by the American
Society of Civil Engineers (ASCE) or the RI State Building Code as
applicable.
d. All new or
significantly expanded recreational boating facilities shall comply with the
policies and prohibitions of §1.3.1(R) of this Part (Submerged aquatic
vegetation and aquatic habitats of particular concern).
9. Marina standards
a. All new or significantly expanded marina
designs shall be in accordance with Table 8 in §1.3.1(D) of this Part
(Minimum Design Criteria), but in no case shall any structural member be
designed to withstand less than one hundred (100) year storm frequency,
including breaking wave conditions in accordance with ASCE 7 (Minimum Design
Loads For Buildings and Other Structures, 2016) and FEMA Manual 55 (Coastal
Construction Manual, 2011) incorporated by reference, not including any further
editions or amendments thereof and only to the extent that the provisions
therein are not inconsistent with these regulations. All design elements
including the bathymetry shall be stamped by a Rhode Island registered Rhode
Island Professional Engineer. Any reconstruction of an existing marina
destroyed by a catastrophic event shall have the piles and float restraint
systems designed to meet the one hundred (100) year storm frequency, while
other elements shall meet the requirements for a fifty (50) year storm at a
minimum.
b. New marinas or any
significant expansion of an existing marina shall first submit a Preliminary
Determination request. The executive director may waive this requirement for
limited marinas when there is minimal expected impact to the resources and no
known use conflicts.
(1) In order to minimize
the impact of the significant expansion within tidal waters, the preferred mode
of expansion shall be dry-stack marina, on the applicant's property or in areas
controlled by the applicant, when consistent with local ordinances.
(2) As part of the requirements under
§1.3.1(A) of this Part (Category B Requirements), the applicant shall
state the basis for the number of wet slips requested.
c. In evaluating the facility proposal, the
applicant must demonstrate that:
(1)
Potential impacts have been or can be avoided to the maximum extent practicable
when considering existing technology, infrastructure, logistics, and costs in
light of approved project purposes; and
(2) Impacts have been or can be minimized to
an extent practicable and appropriate to the scope and degree of those
environmental impacts; and
(3) Any
unavoidable impacts to aquatic and terrestrial resources have been or will be
mitigated to an extent that is practicable and appropriate.
d. The density of in-water vessels
shall be greater than thirty (30) vessels per acre (except in destination
harbors) within the MPL. If vessel density is less than the limit, reduction of
the MPL will be required.
e.
Dockage for dry stack vessel loading and temporary storage shall be excluded
from the marina density calculations, provided only dry stack vessels and
vessels awaiting pump out utilize the area. There shall be no permanent or
transient use of the docks used for dry stack vessels or pumpouts.
f. Marina layout and geometry shall utilize
existing bathymetry to the greatest extent possible. The layout shall provide
for similar size vessels located such that fairway widths can be minimized in
areas of smaller vessels. Fairways shall be a minimum of 1.5-times the length
of the average vessel length utilizing the fairway.
g. The maximum length of any contiguous dock,
both fixed and floating shall be one thousand (1,000) feet for all new or
expanded marinas.
h. Sufficient
sanitary facilities shall be provided to service the patrons of the marina, in
accordance with Table 7 of §1.3.1(D) of this Part (Minimum Required
Sanitary Facilities). The maximum distance from sanitary facilities for any
slip shall be within a one thousand (1,000) foot radius from the facilities.
This may require more than one sanitary facility location. Portable toilets may
be considered sufficient for limited marinas.
i. Marinas with more than two hundred (200)
vessels with an average length in excess of thirty-eight (38) feet may be
eligible for a reduction in the minimum number of facilities at the discretion
of the executive director with an acceptable pump out plan.
(1) Table 7: Minimum required sanitary
facilities
Number of Vessels
|
Toilets
|
Urinals
|
Pump Out locations
|
5 - 25
|
2
|
1
|
1
|
26-100
|
3
|
1
|
1
|
101-200
|
4
|
2
|
2
|
201-250
|
5
|
2
|
3
|
251-300
|
6
|
2
|
3
|
j. Marina owners shall submit documentation
of compliance with the State of Rhode Island's requirements of National Fire
Protection Association (NFPA) 303 Standard for Marinas and Boatyards from the
local or State Fire Official, where appropriate.
k. All electrical installations shall be
designed and installed in accordance with the requirements of the NFPA, State
building and electrical code. The operations & maintenance plan shall
certify that all applicable codes have been met.
l. Sufficient parking shall be provided for
the patrons of the marina. A standard of three hundred (300) square feet is
required for each parking space; the minimum requirements for the total number
of parking spaces provided is one (1) space for each one and one half (1.5)
vessel. If parking for dry stack vessels is in the rack space, no additional
parking is required. On grade Parking for dry stack shall be at one space for
five (5) vessels. Parking for new or expanded marinas in destination harbors
shall be one (1) space for every twenty-five (25) vessels of new or expanded
slips.
m. A Council Assent for a
marina permits the marina operator to undertake minor repairs and alterations
of approved facilities without further review, where such repairs or activities
will not alter the assented design, capacity, purpose or use of the marina. For
the purposes of this section, the assented design, capacity, purpose or use of
the marina shall be those characteristics associated with the physical
configuration or construction, numbers and sizes of vessels accommodated at
in-water facilities, and nature of operation as defined in the original Council
Assent, respectively. Minor repairs and alterations to in-water facilities
shall include repair or replacement of dock decking or planks, replacing
pilings, extensions of slips and/or finger piers within the perimeter and
capacity of the marina as defined within the original Assent, or as established
in §1.3.1(D)(9)(o) of this Part, and other activities of a similar and
non-substantial nature. Minor repairs and alterations to upland facilities may
take place upon Council approval of an operations and maintenance plan as
identified below in §1.3.1(D) (9)(q) of this Part and shall include
grading of parking and launch ramp areas, grouting of seawalls, plumbing and
electrical work, maintenance of sidewalks, fences and walkways, flagpole
installations, landscaping, signage and other activities of a similar and
non-substantial nature. Minor repairs and alterations shall not be construed to
include maintenance dredging, alterations, repairs or expansion of shoreline
protection facilities, bulkheads, or breakwaters or other activities subject to
review under other relevant sections of this program. All minor repairs and
alterations shall take place within the assented design of the marina, or
marina perimeter as defined in the original Council Assent or as established in
accordance with §1.3.1(D)(9)(o) of this Part. Any repair or replacement of
floats for existing marinas shall meet current float design
standards.
n. In those instances
where the minor repair or alteration would require the use of heavy machinery
(such as a pile driver or grader), the Council shall be notified in writing at
least ten (10) working days prior to undertaking the work. Notice of repair
activities requiring the use of heavy machinery shall include the following:
(1) A statement that the notice is given
pursuant to §1.3.1(D)(9) (n) of this Part;
(2) A description of the proposed repair or
alteration to be performed including a statement as to the size and type of
materials to be used;
(3) A copy of
the original Council Assent or Division of Harbors and Rivers permit under
which the proposed repair or alteration is to be performed;
(4) A copy of the site plan from the original
Council Assent showing the location of the proposed repair or
alteration;
(5) The name of the
person on-site responsible for supervising the proposed repair or alteration;
and
(6) The anticipated dates on
which the proposed repair or alteration shall commence and be
completed.
o. All
marinas and/or mooring areas shall have a defined perimeter for in-water
facilities, which shall describe and limit that area in which the repair or
alteration activities described in §§1.3.1(D)(9)(m), 1.3.1(D)(9)(n)
and 1.3.1(D)(9)(p) of this Part may take place. Operators of marinas may apply
to the Council for definition and establishment of this perimeter at any time.
Perimeters shall be defined on the basis of in-water facilities in place as of
September 30, 1971, or subsequently assented structures. All new or modified
Marina Perimeter Limit lines shall be a maximum of ten (10) feet outside of the
marina structures. The MPL shall be designated on all plans with the corners
designated by their State Plane Coordinates.
p. It is permissible to have vessels berthed
at a facility outside of the Marina Perimeter Limit if, in the opinion of the
executive director, there are no conflicts with other users, or impacts to
resources, or conflicts with the DEM Shellfish Program. All vessels shall be
berthed parallel to piers and docks if outside of the MPL. Mediterranean style
mooring (vessel perpendicular to the dock at the stern beyond the MPL) may be
permissible in destination harbors if the executive director determines that
there are no adverse impacts to existing navigation, fishing, commerce or
recreational uses.
q. Proposals for
the alteration or reconfiguration of in-water facilities such as piers and/or
mooring areas shall be reviewed in the following manner:
(1) Alterations to the layout or
configuration of in-water facilities within a previously approved MPL which do
not increase the number of boats accommodated shall obtain a Certification of
Maintenance in accordance with the requirements of §1.3.1(N) of this
Part;
(2) Alterations which propose
to increase the number of boats that may be accommodated at the in-water
facilities of the marina within twenty-five percent (25%) of the capacity of
the marina as defined in the original Council Assent, and do not propose to
extend the facility beyond the defined perimeters (established pursuant to the
original Council Assent or §1.3.1(D)(9)(o) of this Part shall be reviewed
as Category A applications. The Council's review shall establish that the
alterations and/or expansion meet the twenty-five percent (25%) standard, and
that the Council's standards for parking and sanitary facilities are met. If
the twenty-five percent (25%) increase changes the marina type, the expansion
shall be treated as a Category B application and all standards for the new
marina designation shall apply; and
(3) Alterations which propose to increase the
numbers of vessels accommodated at the in-water facilities beyond 25% of the
capacity as defined in the original Council Assent, and/or extend the facility
beyond the defined perimeters, or alter the purpose of the facility shall be
reviewed as a Category B application. The executive director may allow a
onetime expansion of the MPL for limited marinas in Type 2 waters up to
twenty-five percent (25%) of the assented/original boat capacity.
(4) Alterations to marinas in Type 2 waters
shall have all in-water vessels and dry stack vessels count towards the
twenty-five percent (25%) increase in vessel/boat capacity.
r. New marinas and significantly
expanded existing marinas must submit a draft operations & maintenance plan
with their marina permit application. Existing marinas must submit the plan
within one (1) year of the effective date of this regulation. Whenever the
marina ownership or leasehold changes, the O&M plan must be revised and
resubmitted for approval. Plan approvals are valid for three (3) years without
any change in ownership, expansion or major infrastructure work.
s. All O&M plans shall include the
information outlined in the guidance document "Marina Operations and
Maintenance Plans" by the CRMC.
t.
Any Marina that has a "Clean Marina" certification issued by the CRMC will only
be required to submit the facility layout plan (plan requirements in guidance
Document "Marina Operations and Maintenance Plans" by the CRMC and Clean Marina
certification approval letter in lieu of an O&M plan.
u. Any alterations to mooring areas shall be
consistent with any CRMC approved municipal harbor management rules,
regulations or programs, as defined in §1.3.1(O) of this Part.
v. All new marina facilities shall be
required to install a marine pumpout facility. Any significant expansion or
alteration of an existing marina facility that results in greater than or equal
to fifty (50) new slips or where adequate pumpout service is not currently
available shall be required to install a marine pumpout facility. Any expansion
or alteration of an existing marina facility which proposes to increase the
number of vessels accommodated at the in-water facilities beyond twenty-five
percent (25%) of the capacity as defined in the original Council Assent shall
be required to undertake mitigative measures. If twenty-five percent (25%) of
the capacity, as defined in the original Council Assent, is greater than or
equal to fifty (50) slips, then a marine pumpout facility shall be required. If
twenty-five percent (25%) of the capacity, as defined in the original Council
Assent, is less than fifty (50) slips, then the Council shall require either
the installation of a marine pumpout facility or other suitable mitigation
measures. In no case shall the number of pump outs be less than those shown in
Table 7 in §1.3.1(D) of this Part (Minimum Required Sanitary
Facilities).
w. If the applicant
can demonstrate that there are already enough marine pumpout facilities to
serve all of the recreational boating facilities found in the region, then the
Council may waive the requirement for a marine pumpout facility and require
alternative mitigative measures.
x.
All marine pumpout facilities or pumpout stations shall be designed in a manner
that serves the boating public. Pumpout facilities shall be located in an
accessible location. The dock utilized for the pumpout shall not be available
for dockage of any kind beyond the reasonable time for vessel pumpout. In
addition, all marine pumpout facilities shall be open for the general public's
use. However, marina operators may charge a fair and nondiscriminatory fee to
cover the cost of constructing and operating these facilities. Portable
pumpouts (including vessel mounted pumpouts) shall only be allowed after a
facility has one (1) fixed pumpouts in place that meets all requirements.
Portable pumpouts are not considered to satisfy the requirements for a pumpout
except in the case of a Limited Marina.
y. All new marina facilities shall meet the
setback policies and standards contained in municipal harbor management plans
and/or harbor ordinances approved by the Council. However, in all cases marina
facilities shall be setback at least fifty (50) feet from approved mooring
fields and three times the authorized project depth from federal navigation
projects (e.g. navigation channels and anchorage areas).
z. All new or replacement floats shall
utilize floatation that was specifically fabricated for marine use and
warranted by its manufacturer for such use. Foam billets or foam bead shall not
be utilized unless it is completely encapsulated within impact resistant
plastic. All existing installations of non-encapsulated floatation shall be
replaced at a rate of ten percent (10%) per year (minimum) during normal
maintenance. This shall be detailed in the O&M plan. The start of mandatory
replacement shall begin in October 2011.
aa. All new marinas (including expansions)
and water dependent facilities shall be designed in accordance with the latest
Accessible Boating Facilities Guidelines by the United States Access Board
promulgated under 36 C.F.R. Part 1191 . The number of fully accessible slips
shall be in accordance with the latest version of the guidelines, but in no
case shall be less than 2% of the facility. Limited Marinas are not required to
meet the accessibility guidelines, but are encouraged to do so.
bb. The executive director, in his
discretion, shall have the authority to determine which of the above standards
shall be applied to Limited Marinas.
10. Launching ramp standards
a. All public launching ramps shall be
designed to allow emergency vehicle turning at the top of the ramp. The ramp
shall be designed with two (2) areas to allow vessel prep and tie down in close
proximity of the haul/launch area. All parking for boat trailers shall be
angled only, with a strong preference for pull through parking. All ramps shall
have clearly marked parking for car top vessel parking.
b. Ramps shall be constructed at an angle no
greater than fifteen percent (15%) from the horizontal. Where upland
modification is necessary, the slope will be created, where possible, by
cutting back into the upland, rather than by placing fill on a shoreline
feature. Ramps shall be approximately even with beach grade.
c. All new or reconstructed public ramps
shall extend a sufficient distance inland to prevent washout at the inland edge
and shall extend a minimum of four (4) feet beyond extreme low water.
Single-lane ramp width shall not be less than fifteen (15) feet.
d. Side slopes of the ramp (above water line)
shall be constructed of sloped riprap or, if the slope permits,
vegetated.
11.
Residential and limited recreational docks, piers, and floats standards
a. All residential and limited recreational
dock designs shall be in accordance with Table 8 in §1.3.1(D) of this Part
(Minimum design criteria), but in no case shall any structural member be
designed to withstand less than fifty (50) year storm frequency, including
breaking wave conditions in accordance ASCE 7 ( Minimum Design Loads For
Buildings and Other Structures, 2016) and FEMA Manual 55 (Coastal Construction
Manual, 2011) incorporated by reference, not including any further editions or
amendments thereof and only to the extent that the provisions therein are not
inconsistent with these regulations. All design elements including the
bathymetry shall be stamped by a Rhode Island registered professional
engineer.
b. Applications for all
residential and limited recreational boating facilities shall indicate all work
associated with these structures including at a minimum: a bottom survey
showing water-depth contour lines and sediment types along the length of the
proposed structure the seaward and landward extent of any SAV or coastal
wetland vegetation present at the site, the permitted/authorized dimensions of
any CRMC buffer zone and/or access way, as well as all associated work involved
in accessing the proposed facility. All pathways, boardwalks, and cutting or
filling of coastal features shall be specified. All such work shall be in
accordance with applicable standards in §§1.3.1(B) and 1.3.1(C) of
this Part. All of the above work shall be certified by a Professional Engineer
licensed in the State of Rhode Island.
c. Fixed structures which are for pedestrian
access only shall be capable of supporting forty (40) pounds per square foot
live load as well as their own dead weight; floating structures shall be
capable of supporting a uniform twenty (20) pounds per square foot live load,
or a concentrated load of four hundred (400) pounds. A written certification by
the designer that the structure is designed to support the above design loads
shall be included with the application.
d. No creosote shall be applied to any
portion of the structure.
e. A
residential or limited recreational boating facility shall be a maximum of four
(4) feet wide, whether accessed by a fixed pier or float. The terminal float
size shall not exceed one hundred fifty (150) square feet and may be reviewed
as a Category A application. Residential boating facilities shared by owners of
waterfront property may have a maximum of two (2) terminal floats not to exceed
a combined total terminal float area of three hundred (300) square feet. Such
applications may be reviewed as a Category A application. In excessive fetch
areas only, the terminal float size shall not exceed two hundred (200) square
feet and shall be reviewed as a Category B application. The combined terminal
float size for shared residential boating facilities shall not exceed three
hundred (300) square feet regardless of fetch. In the absence of a terminal
float, a residential boating facility may include a fixed terminal T or L
section, no greater than four (4) by twenty (20) feet in size.
f. All new or replacement floats shall
utilize floatation that was specifically fabricated for marine use and
warranted by its manufacturer for such use. Foam billets or foam bead shall not
be utilized unless they are completely encapsulated within impact resistant
plastic.
g. Where possible,
residential boating facilities shall avoid crossing coastal wetlands. In
accordance with§1.3.1(Q) of this Part, those structures that propose to
extend beyond the limit of emergent vegetative wetlands are considered
residential boating facilities. Facilities shall be located along the shoreline
so as to span the minimal amount of wetland possible. Facilities spanning
wetlands shall be elevated a minimum of four (4) feet above the marsh substrate
to the bottom of the stringers, or constructed at a 1:1 height to width ratio.
Construction in a coastal wetland shall be accomplished by working out from
completed sections. When pilings are placed within coastal wetlands, only the
immediate area of piling penetration may be disturbed. Pilings should be spaced
so as to minimize the amount of wetland disturbance. No construction equipment
shall traverse the wetland while the facility is being built.
h. Owners are required to maintain their
facilities in good working condition. Facilities may not be abandoned. The
owner shall remove from tidal waters and coastal features any structure or
portions of structures which are destroyed in any natural or man-induced
manner. CRMC authorization for a recreational boating facility allows a dock
owner to undertake minor repairs of approved facilities without further review,
where such repairs will not alter the assented and/or permitted design,
capacity, purpose or use of the facility. For the purposes of this policy,
minor repairs shall include the repair or replacement of dock decking or
planks, hand railings and support, and other activities of a similar and
non-substantial nature. Minor repairs do not include alterations to the
approved design of the facility, expansion of the facility, or work requiring
the use of heavy machinery, such as a pile driver; these activities require
that a Certification of Maintenance be obtained from the Council.
i. Float ramps and other marine appurtenances
or equipment shall not be stored on a coastal feature or any area designated as
a CRMC buffer zone.
j. The use of
cribs for structural support shall be avoided. The use of cribs as support in
tidal waters may be permitted given certain environmental design
considerations. However, in these instances the size and square footage shall
be minimized and not exceed six (6) feet by six (6) feet in footprint dimension
and the structure cannot pose a hazard to navigation. When cribs are permitted
for structural support, they must be removed when the useful life of the
structure has ceased (e.g. the structure is no longer used as a means of
accessing tidal waters).
k.
Residential and limited recreational boating facilities shall not intrude into
the area within twenty-five (25) feet of an extension of abutting property
lines unless:
(1) It is to be common
structure for two or more adjoining owners, concurrently applying or
(2) A letter or letters of no objection from
the affected owner or owners are forwarded to the CRMC with the
application.
(3) In the event that
the applicant must seek a variance to this standard, the variance request must
include a plan prepared by a RI registered Land Surveyor which depicts the
relationship of the proposed facility to the effected property line(s) and
their extensions. Following construction the applicant shall submit an as-built
plan stamped by a RI registered land surveyor showing the as-built location
along with the CRMC designer's dock as-built form required by
§1.3.1(D)(11)(t) of this Part. Any discrepancy from the CRMC approved dock
location will require relocation of the dock to the approved
location.
l. Residential
and limited recreational boating facilities shall not extend beyond that point
which is:
(1) Twenty-five percent (25%) of
the distance to the opposite shore (measured from mean low water), or
(2) Fifty (50) feet seaward of mean low
water, whichever is the lesser.
m. All residential and limited recreational
docks, piers, and floats shall meet the setback policies and standards
contained in municipal harbor management plans and/or harbor ordinances
approved by the Council. However, in all cases, residential and limited
recreational docks, piers, and floats shall be setback at least fifty (50) feet
from approved mooring fields and three-times the U.S. Army Corps of Engineers
authorized project depth from federal navigation projects (e.g., navigation
channels and anchorage areas).
n.
No sewage, refuse, or waste of any kind may be discharged from the facility or
from any vessel utilizing it.
o. A
Council Assent for a residential or limited recreational boating facility
permits the owner to undertake minor repairs of approved facilities without
further review, where such repairs will not alter the assented and/or permitted
design, capacity, purpose or use of the facility. For the purposes of this
section, minor repairs shall include the repair or replacement of dock decking
or planks, hand railings and support, and other activities of a similar and
non-substantial nature. Minor repairs do not include alterations to the
approved design of the facility, expansion of the facility, or work requiring
the use of heavy machinery (such as a pile driver); these activities require
that a Certification of Maintenance be obtained from the Council in accordance
with §1.3.1(N) of this Part. Residential boating facilities shall be in
continuous and uninterrupted use to meet this standard, in accordance with
permit conditions.
p. Materials
used for the construction of residential and limited recreational boating
facilities shall not include steel or concrete piles.
q. The surface of the dock, pier and float
shall be designed in a manner which provides safe traction and allows for the
appropriate drainage of water.
r.
Geologic site conditions shall exist which are appropriate for driven pile
structural support.
s. As part of a
residential or limited recreational boating facility, the terminal float may be
designed such that it facilitates the access of small vessels such as kayaks,
dinghies, personal water craft, etc., onto the float, provided that all other
programmatic requirements are met. Mechanical apparatus to accomplish this
shall not exceed twenty-four (24) inches in height from the top of the
float.
t. All applicants for
residential and limited recreational docks shall submit the CRMC designer's
dock as-built form and an as-built survey within thirty (30) days following
construction. The as-built survey shall show the following:
(1) Location of the dock in relation to the
property lines;
(2) The most
seaward end of the dock marked in state plane coordinates; and
(3) The as-built length and width including
all terminal floats and boat lifts.
u. Recreational boating facilities other than
marinas and those facilities associated with residential development, where
applicable, shall follow the design standards contained herein including those
described in Table 8 in §1.3.1(D) of this Part.
v. Lateral access shall be provided under,
around or over as appropriate for the site conditions at all new residential
docks.
w. In order to minimize
impacts to existing areas of submerged aquatic vegetation (SAV) habitat, new
residential boating facilities or modifications to existing residential boating
facilities shall be designed in accordance with the guidelines and standards
contained within §1.3.1(R) of this Part, as most recently revised.
Facilities shall be located along the shoreline so as to impact the minimal
amount of habitat possible.
x. The
long-term docking of vessels at a recreational boating facility shall be
prohibited over SAV. Such facilities shall be used for touch and go
only.
y. All residential and
limited recreational boating facilities must have affixed to them a
registration plate and number located on the seaward face of the most seaward
piling. If a facility does not have pilings and/or is generally a floating
structure, or is built on crib supports, then the registration plate must be
affixed to the seaward face of the most seaward dock or floating dock.
Regardless of the type of residential or limited recreational boating facility
structure, the registration plate and number must be permanently affixed to the
facility on its most seaward face and be visible from the navigation channel or
fairway to the structure at all times.
z. Table 8: Minimum design criteria
Min. pile tip diameter
|
10"
|
Min/max float freeboard
|
8"/30"
|
Min. pile butt diameter
|
12"
|
Maximum fetch for residential docks
|
4 miles
|
Marina minimum pile embedment
|
15 feet
|
Minimum stringer/Joist
|
3"x10"
|
Residential minimum pile embedment
|
10 feet
|
Minimum through bolt hardware diameter - hot
dipped galvanized
|
3/4"
|
Minimum marina deck and float load
|
60 psf LL
500 lb concentrate d
|
Minimum cross bracing
|
3"x10"
|
Residential deck load
|
40 PSF LL
400 LB concentrated
|
Minimum lag bolt diameter
|
1/2"
|
Min float freeboard
*including LL and DL
|
12"
|
Minimum water depth at the terminus of
recreational boating facilities
|
18" MLW
|
Design wind loads
|
wind gust based on 50 year return and natural
period of 60 seconds
|
Required datum
|
MLW
|
Wave conditions (min)
|
All fixed and floating structure shall be
designed for a 3' minimum
|
Min pile cut off
|
V zone elevation + float freeboard + 1'
|
12. Residential and limited recreational
docks with excessive fetch standards
a. A
location shall be considered to have excessive fetch if there is a twenty
degree (20º) sector over four (4) miles in any direction in which wind can
blow over the water to generate waves.
b. Boat lifts, suitably designed and
installed, are encouraged for docks with excessive fetch.
c. Residential and limited recreational docks
with excessive fetch shall provide uplift calculations as part of the required
calculation package.
d. All
structural elements, including the boat lift, shall be designed to withstand
the one hundred (100) year storm frequency, including breaking wave conditions
in accordance with ASCE 7 (Minimum Design Loads For Buildings and Other
Structures, 2016) and FEMA Manual 55 (Coastal Construction Manual, 2011)
incorporated by reference, not including any further editions or amendments
thereof and only to the extent that the provisions therein are not inconsistent
with these regulations.
e. All
residential and limited recreational docks with excessive fetch shall have an
as-built plan on file with the CRMC within thirty (30) days of construction
that certifies conformance with the approved plans.
f. All residential and limited recreational
docks with excessive fetch shall be inspected and certified every five (5)
years by a Registered Professional Engineer licensed in Rhode Island that all
elements of the dock and lift system meet the requirements of ASCE 7 (Minimum
Design Loads For Buildings and Other Structures, 2016) or FEMA Manual 55
(Coastal Construction Manual, 2011) incorporated by reference, not including
any further editions or amendments thereof and only to the extent that the
provisions therein are not inconsistent with these regulations.
13. Residential and limited
recreational boating facilities - Violations
a. If a registration plate is not present on
a recreational boating facility structure, the CRMC will inform the owner in
writing that the owner must secure a registration plate on the dock in
accordance with the requirements herein. The dock owner will have 45 days to
respond to this written notice. The CRMC may invoke enforcement actions and its
fine and fee schedules as specified below.
b. Enforcement actions shall be registered on
land evidence records. Upon proof that an enforcement action has been
satisfactorily addressed by a property owner in violation of these provisions,
the CRMC will notify the property owner in writing that the violation may be
removed from the land evidence records. The property owner may then cause the
enforcement action to be removed from the land evidence records and shall
notify the CRMC and show proof of such removal by registered letter.
c. Each issuance of violation is considered
to be a new violation, and subject to the following fine schedule.
14. Residential and limited
recreational boating facilities - Fine schedule
a. Registration plate not posted:
$1,000
b. Use of plate not
registered to dock: $1,000
c.
Non-compliance with assent/permit stipulations: Up to $1,000
d. Non-compliance with §1.3.1(D) of this
Part: Up to: $1,000
e. Each
subsequent violation: Up to: $1,000 per violation
f. Lost or stolen plates not reported within
60 days: $100
F.
Treatment of sewage and stormwater
1.
Policies
a. It is the Council's policy to
maintain and, where possible, improve the quality of coastal wetlands,
contiguous freshwater wetlands, freshwater wetlands in the vicinity of the
coast, groundwater resources and tidal and salt pond surface waters. In so
doing, the Council requires the use of low impact development (LID) strategies
as the primary method of stormwater management to reduce the volume of
stormwater runoff to surface waters, recharge groundwater supplies, and improve
overall water quality.
b. It is the
Council's policy to minimize the amount of onsite wastewater treatment system
(OWTS) derived nitrates and other potential contaminants which may leach into
salt ponds and all other Type 1, 2, and 3 waters.
c. The Council encourages applicants for a
CRMC Assent to install, alter or repair an OWTS to meet on site with CRMC staff
prior to undertaking of OWTS groundwater and soil tests to discuss the location
of the system and buffer zones, where applicable.
d. It is the Council's policy to require the
proper management and treatment of stormwater through the preparation and
implementation of a stormwater management plan in accordance with the most
recent version of RIDEM Rhode Island Stormwater Design and Installation
Standards Manual, and which satisfies the requirements of the RICRMP and any
applicable Special Area Management Plan.
e. The most recent version of the RIDEM Rhode
Island Stormwater Design and Installation Standards Manual provides the
appropriate methods for the preparation of stormwater management plans and the
treatment of stormwater using LID practices and methods within the CRMC's
jurisdiction. The Council also recognizes that the most recent version of the
Rhode Island Soil and Erosion and Sediment Control Handbook (
http://www.dem.ri.gov/programs/water/permits/ripdes/stormwater/s
oil-erosion.php), and its amendments, published jointly by the Rhode
Island Department of Environmental Management and the United States Department
of Agriculture (USDA), Natural Resources Conservation Service (NRCS) provides
additional guidance and supplemental information with respect to the management
and treatment of stormwater.
f. It
is the Council's policy that all stormwater management plans shall take into
consideration all potential impacts associated with the discharge of stormwater
runoff into the coastal environment. Potential impacts include, but are not
limited to, the following:
(1) Impacts to
salt marshes such as changes in species composition due to the introduction of
freshwater to high marsh areas;
(2)
Changes in the salinity of receiving waters;
(3) Thermal impacts to receiving
waters;
(4) The effects of
introducing stormwater runoff to receiving waters with low dissolved oxygen
concentrations; and
(5) Other
potential water quality impacts.
g. The Council's policy is to ensure that all
projects are planned, designed, and developed in order to:
(1) Protect areas that provide important
water quality benefits and/or are particularly susceptible to erosion and
sediment loss;
(2) Limit increases
of impervious surface areas, except where absolutely necessary;
(3) Limit land disturbance activities such as
clearing and grading and cut and fill to reduce erosion and sediment loss;
and
(4) Limit disturbance of
natural drainage features and vegetation. Additionally, stormwater management
practices should be designed as landscape amenities to include native plant
species on project sites. The Council recommends applicants to use the "Rhode
Island Coastal Plant Guide," an interactive, web-based plant list prepared by
the URI Cooperative Extension Education Center in consultation with the CRMC
and available online at:
www.crmc.ri.gov/coastallandscapes.html.
h. To show that a proposed
development has met a standard to the maximum extent practicable, the applicant
must demonstrate the following:
(1) All
reasonable efforts have been made to meet the standard in accordance with
current local, state, and federal regulations;
(2) A complete evaluation of all possible
management measures has been performed; and
(3) If full compliance cannot be achieved,
the highest practicable level of management is being implemented.
2. Prerequisites
a. Applicants seeking a Council Assents to
construct, alter, or repair onsite wastewater treatment systems or point source
discharges shall first obtain the requisite permit(s) from the Department of
Environmental Management.
b. The
discharge standards, effluent limitations and pretreatment standards
established for the discharge of pollutants to waters of the State under the
Rhode Island Pollutant Discharge Elimination System (RIPDES) program, and
administered by the Department of Environmental Management (DEM), are the
State's water pollution control requirements. Applicants for projects for which
an Individual RIPDES Permit is required shall obtain said permit from DEM and
submit the Individual RIPDES Permit with the CRMC Assent application. Note:
Projects that are eligible to submit a Notice of Intent (NOI) for coverage
under a RIPDES General Permit are not required to submit the RIPDES
Authorization with the CRMC Assent application. Applicants for such projects,
however, are encouraged to file a Notice of Intent (NOI) with DEM concurrently
with their CRMC application to allow a coordinated review between the
agencies.
c. The Council shall
formally review proposed actions only after all other applicable state/local
requirements have or will be met. The Council, however, will comment on
preliminary plans for major facilities to assist in the planning
process.
d. The Executive Director
or the Council may require that an applicant obtain a DEM System Suitability
Determination, as provided in the DEM OWTS Rules (250-RICR- 150-10-6), for
onsite wastewater treatment systems that pre-date 1968.
3. Prohibitions
a. Point source discharges of sewage and/or
stormwater runoff are prohibited on unconsolidated coastal banks and
bluffs.
b. New and enlarged
stormwater discharges to the high salt marsh environment bordering Type 1 and
Type 2 waters and within salt marshes designated for preservation which border
Type 3, 4, 5, and 6 waters are prohibited. Stormwater discharges to existing
well flushed tidal channels within high marshes shall not be subject to this
prohibition. All such discharges, however, shall meet the applicable standards
contained herein.
c. Point source
discharges of sewage are prohibited in Type 1 waters.
4. Standards
a. For Onsite Wastewater Treatment Systems
(OWTS):
(1) See standards in §1.3.1(B) of
this Part (Filling, removing, or grading).
(2) The construction, repair or alteration of
all OWTS and components shall conform to the standards set forth in the most
recent RIDEM Rules Establishing Minimum Standards relating to Location, Design,
Construction and Maintenance of Onsite Wastewater Treatment Systems promulgated
by the Department of Environmental Management (referred to herein as DEM OWTS
Rules (250-RICR- 150-10-6)).
(3)
Site grading around the OWTS shall direct the flow of surface runoff water away
from the OWTS and meet all applicable requirements of the DEM OWTS
Rules.
(4) Sub-drains constructed
to lower groundwater levels in an area where an OWTS will be located shall:
(AA) Conform to all applicable DEM
rules;
(BB) Have no piping located
between the anticipated OWTS and the shoreline; and
(CC) Have exposed outfalls suitably protected
against shoreline erosion and scour.
(5) When new construction, renovation or a
change of use is proposed for existing buildings, an OWTS Suitability
Determination shall be obtained by the applicant from the Department of
Environmental Management to indicate that the existing OWTS meets all
applicable DEM OWTS Rules or the applicant shall submit a building official
document indicating that a DEM OWTS Suitability Determination is not
required.
(6) Connections to OWTS
and cesspools that are abandoned shall be removed, blocked, or otherwise
disconnected, and abandoned cesspools and septic tanks shall be pumped dry and
filled with clean fill in accordance with all applicable DEM OWTS
Rules.
(7) Where necessary,
barriers shall be constructed to prevent vehicles from passing or parking over
septic systems, unless permissible in accordance with DEM OWTS Rules.
(8) The repair of OWTS along the Rhode Island
south shore from Watch Hill to Narragansett shall conform to the DEM "OWTS
Repair Guidance in Critical Erosion Areas."
b. The requirements of the RIDEM Stormwater
Management, Design and Installation Rules (250-RICR- 150-10-8) shall apply to
all CRMC applications.
c. For
stormwater management the Council requires, in accordance with the "Smart
Development for a Cleaner Bay Act of 2007" (see R.I. Gen. Laws Chapter
45-61.2), that all applicable projects meet the following requirements:
(1) Maintain pre-development groundwater
recharge and infiltration on site to the maximum extent practicable;
(2) Demonstrate that post-construction
stormwater runoff is controlled, and that post-development peak discharge rates
do not exceed pre-development peak discharge rates; and
(3) Use low impact-design techniques as the
primary method of stormwater control to the maximum extent
practicable.
d.
Residential, commercial, industrial or public recreational structures as
defined in §1.3.1(C) of this Part shall provide treatment and management
of stormwater runoff for all new structural footprint expansions, including
building rooftops, greater than six (600) hundred square feet in size and any
new impervious pavement, driveways, sidewalks, or parking areas, regardless of
size. Applicable projects shall submit a stormwater management plan that
demonstrates compliance with the eleven (11) minimum stormwater management
standards and performance criteria as detailed in the most recent version of
the RIDEM Rhode Island Stormwater Design and Installation Standards Manual.
Single-family dwelling projects, however, may meet these provisions as detailed
below in §§1.3.1(F)(3)(h) and (i) of this Part, below.
e. Roadways, highways, bridges, and other
projects subject to §1.3.1(M) of this Part shall provide treatment and
management of stormwater runoff for all new impervious surfaces. These projects
shall submit a stormwater management plan that demonstrates compliance with the
eleven (11) minimum stormwater management standards and performance criteria as
detailed in the most recent version of the RIDEM Rhode Island Stormwater Design
and Installation Standards Manual. Any improvement projects to existing roads,
highways and bridges and other projects subject to §1.3.1(M) of this Part
that result in the creation of new impervious surfaces shall provide treatment
and management of stormwater as above for all new impervious surfaces.
Maintenance activities such as pavement resurfacing projects, replacement of
existing drainage systems, minor roadway repairs, or emergency roadway and
drainage repairs are excluded from these requirements provided the project does
not result in an expansion of the existing impervious surface area, new or
enlarged stormwater discharges, or the removal of roadway materials down to the
erodible soil surface of ten thousand (10,000) square feet or more of existing
impervious area.
f. Unless exempted
as a maintenance activity herein, any redevelopment that disturbs ten thousand
(10,000) square feet or more of existing impervious surface coverage shall
comply with Minimum Stormwater Standard 6: Redevelopment and Infill Projects of
the RIDEM Stormwater Management, Design and Installation Rules (250-RICR-
150-10-8). Maintenance activities subject to §1.3.1(N) of this Part are
excluded from these requirements provided there is no expansion of the existing
impervious surface area and no new or enlarged stormwater discharges resulting
from the maintenance activity.
g.
All stormwater management plans shall take into consideration potential impacts
associated with the discharge of stormwater runoff into the coastal
environment. Applicants shall address these potential impacts to include, but
not limited to, the following:
(1) Impacts to
coastal wetlands such as changes in species composition due to the introduction
of freshwater to high marsh areas;
(2) Changes in the salinity of tidal
receiving waters;
(3) Thermal
impacts to receiving waters;
(4)
Effects of introducing stormwater runoff to receiving waters that have low
dissolved oxygen concentrations; and
(5) Other potential water quality impacts as
may be identified by CRMC staff.
h. Applicants for single-family residential
dwellings and accessory structures shall treat the stormwater runoff water
quality volume (WQv) from all new building rooftops greater than six (600)
hundred square feet in size and any new impervious driveways and parking areas,
regardless of size. All dwelling and accessory structure rooftop expansions
constructed within a twelve (12) month period shall be counted towards the six
hundred (600) square foot threshold. Once the six hundred (600) square foot
threshold is exceeded, stormwater management must be provided for all rooftop
expansions constructed within that 12-month period. Applicants for
single-family dwelling projects may use the design guidance and performance
criteria in the most recent version of the RIDEM Stormwater Management, Design
and Installation Rules (250-RICR- 150-10-8) or the most recent version of the
RI Stormwater Management Guidance for Individual Single-Family Residential Lot
Development. Applicants for single-family dwellings and accessory structures on
CRMC-designated barriers shall manage stormwater runoff as provided in
§1.3.1(F)(4)(i) of this Part below. Pretreatment of stormwater runoff is
not required for single-family residential applications.
i. Applicants for single-family dwellings and
accessory structures located on CRMC-designated barriers shall manage
stormwater runoff as follows:
(1) Runoff from
rooftops shall be directed by non-erosive sheet flow onto vegetated areas
surrounding the dwelling or accessory structure; and
(2) Construction of driveway and parking
surfaces shall be limited to crushed stone, crushed shell, open plastic grid
systems filled with sand, gravel or vegetation, or any combination of the
preceding, to prevent damage to other properties during major storm events.
Stormwater runoff shall be directed by non-erosive sheet flow onto vegetated
areas alongside the driveway or parking area.
j. New or enlarged stormwater discharges to
salt marshes and well flushed tidal channels within high marshes shall only be
permitted when the applicant can clearly demonstrate that no reasonable
alternatives exist (e.g., no other discharge locations having a gravity flow
outlet are available and impervious surfaces have been kept to an absolute
minimum) and when no adverse impacts to the salt marsh will result. In these
instances, the applicant shall meet all applicable standards contained in the
RIDEM Stormwater Management, Design and Installation Rules (250-RICR-
150-10-8). This standard does not apply to low salt marsh environments with an
average width along the property of less than thirty-five (35) feet.
k. Stormwater open drainage and pipe
conveyance systems must be designed to provide adequate passage for flows
leading to, from, and through stormwater management facilities for at least the
ten (10) year, twenty-four (24) hour Type III storm event. Applicants may not
be required to control post-development peak discharge rates at pre-development
peak discharge rates provided the project design provides for non-erosive
stormwater discharges to tidal waters.
l. Applicants may be required to submit a
pollutant loading analysis to demonstrate that a proposed project will not
unduly contribute to, or cause, water resource degradation when such projects
are located in sensitive coastal resource areas. When a pollutant loading
analysis is required, the applicant shall use the method detailed in the RIDEM
Stormwater Management, Design and Installation Rules (250-RICR- 150-10-8). If
the Council determines that any proposed stormwater discharge will result in an
unacceptable discharge of pollutants to the tidal waters of Rhode Island, the
Council shall require the applicant to mitigate the pollutant loads to
acceptable levels using the practices detailed in the stormwater rules.
Frequently, this can be accomplished using these practices in series to achieve
higher pollutant removal efficiencies.
m. The use of proprietary hydrodynamic
(swirl) separator or filter devices shall be limited to pre-treatment
applications only, unless the device has met the requirements of the Technology
Assessment Protocol (TAP) as detailed in the RIDEM Stormwater Management,
Design and Installation Rules (250-RICR- 150-10-8). The CRMC may, however,
approve such devices in situations where end-of-pipe retrofit solutions are the
only alternative available when site constraints limit the use of standard low
impact development methods for the treatment and management of stormwater
runoff. In such circumstances, however, the use of such proprietary devices
shall conform to the standards and performance criteria set forth in the most
recent version of the RIDEM Stormwater Management, Design and Installation
Rules (250-RICR- 150-10-8) to the maximum extent practicable.
n. For outfalls:
(1) Work on outfalls, drainage channels,
etc., shall proceed from the shoreline toward the upland in order that no
unfinished or un-stabilized lower channel portions be subjected to
erosion-producing velocities from upstream. If this cannot be accomplished, all
flow shall be diverted from the unfinished areas until stabilization is
completed.
(2) Where possible,
outfall pipe slopes shall be designed for an exit velocity of less than five
(5) feet per second.
(3) Screens or
grates shall be placed over the end of large outfalls to trap debris.
(4) Beaches or other coastal features in
front of outfalls shall be returned to original grade.
(5) Riprap placed on beaches shall not
increase the grade of the beach higher than one foot in order to maintain
lateral access below mean high water.
(6) Riprap shall be compact, hard, durable,
angular stone, with an approximate unit weight of one hundred sixty-five (165)
lbs./cubic foot.
(7) Riprap shall
be placed with an adequate bedding of crushed rock or other suitable filtering
material.
o. Applicants
with new or modified single-family dwelling projects subject to the stormwater
management provisions herein shall submit the following information:
(1) 8.5 x 11 inch site plan depicting the
location of all structural stormwater (LID or otherwise) components;
and
(2) Operation & Maintenance
Plan consistent with CRMC guidance to ensure long-term maintenance and
operation of the stormwater structural practice(s) on the site.
p. Applicants for all other
projects subject to the stormwater management provisions herein shall submit
the following information:
(1) 8.5 x 11 inch
site plan depicting the location of all structural stormwater (LID or
otherwise) components;
(2)
Operation & Maintenance Plan that meets the specifications detailed in the
most recent version of the RIDEM Rhode Island Stormwater Design and
Installation Standards Manual; and
(3) Following completion of the approved
project, a post-construction certification by a Rhode Island registered P.E.
and Rhode Island registered Landscape Architect, where required, demonstrating
that all stormwater structures, LID components, and requisite planting
materials necessary for the function of the stormwater management system were
installed in accordance with the approved permit, specifications and approved
site plans.
G. Shoreline protection
1. Policies
a. The Council prefers nonstructural
shoreline protection methods over all other shoreline protection methods for
controlling erosion such as stabilization with vegetation and beach nourishment
due to their effectiveness in preserving beaches, natural shoreline habitats
and sediment dynamics.
b. In most
cases the Council prefers hybrid shoreline protection methods over structural
shoreline protection methods due to their effectiveness in preserving beaches,
natural shoreline habitats and sediment dynamics as compared to structural
shoreline protection.
c. Where
structural shoreline protection may be authorized riprap revetments are
preferred to vertical steel, timber, or concrete seawalls and bulkheads except
where vertical structures may be proposed to service ports, marinas and other
water dependent uses bordering Types 3, 5 and 6 waters. All of these forms of
structural shoreline protection are considered to be permanent, not temporary
structures.
d. When structural
shoreline protection is proposed, the Council shall require that the owner
exhaust all reasonable and practical alternatives including, but not limited
to, the relocation of the structure(s) intended to be protected, landward
re-contouring of the shoreline to create a more dissipative profile, and
nonstructural and hybrid shoreline protection methods.
e. Any sheet pile walls, concrete or stone
walls, or other structures that are located within the fifty (50) foot minimum
setback or the erosion setback pursuant to § 1.1.9 of this Part and which
would extend to a depth below grade to protect land or structures from active
or future shoreline erosion shall be defined as structural shoreline
protection. Such structures shall comply with the policies, prerequisites,
prohibitions, and standards of this Part.
f. Pursuant to § 1.3.6 of this Part, new
shoreline protection shall be designed and constructed to not unreasonably
interfere with the public's right to lateral shoreline access, as the public
has a right to lateral access along the shoreline as provided within the Rhode
Island Constitution. It is the Council's policy to require applicants to
provide appropriate on-site access of a similar type and level to that which
will be impacted by the project.
2. Prerequisites
a. Permits for hybrid or structural shoreline protection projects
with any portion of the project located below the high tide line must be
obtained concurrently from the Army Corps of Engineers and the CRMC. Army Corps
and CRMC requirements are designed to complement one another; applicants should
consider the requirements of both agencies when beginning the permit process.
In some cases, the CRMC may require an applicant to obtain applicable Army
Corps of Engineers permits prior to applying to the Council. A CRMC Assent is
not valid unless the applicant has received all required Army Corps of
Engineers approvals. For purposes of federal consistency the CRMC shall require
applicants to submit a copy of the completed Army Corps of Engineers
application to the CRMC to partially fulfill the federal requirements pursuant
to 15 C.F.R. § 930.
b. Hybrid or structural shoreline protection
projects that require an Army Corps of Engineers permit or that are located
below the high tide line also require a RI Department of Environmental
Management water quality certification. A CRMC assent is not valid unless the
applicant has received all required RI Department of Environmental Management
approvals.
3.
Prohibitions
a. The Council shall prohibit
new hybrid and structural shoreline protection on barriers classified by the
CRMC as undeveloped, moderately developed, and developed as well as shorelines
abutting Type 1 waters, unless the shoreline is determined by the CRMC to be a
manmade shoreline as defined within § 1.1.2 of this Part or is permissible
under § 3.4.12 of this Subchapter.
b. The Council shall prohibit the use of
hybrid or structural shoreline protection to protect undeveloped land or
structures not integral to the primary structure.
c. Filling on a coastal feature or tidal
waters beyond that which is consistent with §1.3.1(G)(5)(a) of this Part
is prohibited.
d. Shoreline
protection is prohibited when proposed to be used to regain property lost
through historical erosion or storm events, unless the project is a marsh sill
designed for wave attenuation as part of a marsh creation, enhancement, or
restoration project.
e. The
construction of new seawalls and bulkheads is prohibited, except for shorelines
bordering Types 3, 5 and 6 waters where the proposed seawall or bulkhead
directly serves a water-dependent use or where an applicant demonstrates to the
satisfaction of the CRMC that there is no technically feasible
alternative.
4.
Additional Category B Requirements
a.
Applicants for new hybrid shoreline protection shall, on the basis of sound
professional information, demonstrate in writing all of the following:
(1) An erosion hazard exists due to natural
erosion processes and the proposed hybrid shoreline protection has a reasonable
probability of controlling this erosion problem;
(2) Nonstructural shoreline protection has
not worked in the past or will not work in the future because these methods are
not suitable for the site conditions;
(3) There are no practical or reasonable
alternatives to the proposed activity such as the relocation of existing
structures that would relieve the need for hybrid shoreline
protection;
(4) The proposed
practice is not likely to increase erosion or disrupt shoreline sediment
dynamics that sustain adjacent natural shoreline features and the stability of
the shoreline on either side of the project;
(5) Describe the long-term maintenance plan
for the hybrid shoreline protection project including addressing storm damage;
and
(6) Plans for hybrid shoreline
protection practices shall be prepared by an appropriate design professional
(e.g., registered professional engineer, landscape architect or land surveyor).
b. Applicants for
structural shoreline protection measures to control erosion shall, on the basis
of sound professional information, demonstrate in writing all of the following:
(1) An erosion hazard exists due to natural
erosion processes and the proposed structural shoreline protection has a
reasonable probability of controlling this erosion problem;
(2) Nonstructural and hybrid shoreline
protection has not worked in the past or will not work in the future because
these methods are not suitable for the present site conditions;
(3) There are no practical or reasonable
alternatives to the proposed activity such as the relocation of existing
structures that mitigate the need for structural shoreline
protection;
(4) The proposed
structure is not likely to increase erosion or disrupt shoreline sediment
dynamics that sustain adjacent natural shoreline features, or adversely affect
the stability of the shoreline on either side of the project;
(6) Describe the long-term maintenance
program for the structure including storm damage, the ability to rebuild the
structure following storm damage and financial commitments to pay for said
maintenance;
(7) New structural
shoreline protection shall be designed and certified by a registered
professional engineer; and
(8)
Describe all likely impacts that the structural shoreline protection may have
on the continued public lateral beach access. If lateral public access will be
impacted at any time, a lateral public access plan shall be provided, except
where preempted by federal law (e.g., U.S. Coast Guard Maritime Security
(MARSEC)).
c. Applicants
for breakwaters and jetties in addition to §1.3.1(G)(a) and (b) of this
Part above shall demonstrate that the proposed structure is necessary to
provide protection to a marina, port facility, public mooring area, or public
beach area.
d. Applicants for
breakwaters and jetties shall also provide an evaluation of the structure's
potential for interrupting the longshore movements of sediment. If such an
interruption is likely to be significant, the applicant shall design a sand
bypass system or another measure that will assure that the effects on sediment
transport shall not cause significant erosion or interrupt sediment supply to
adjacent natural shoreline features. Where it is determined a sand bypass
system is necessary, but will not be practicable or functional considering the
site conditions, the Council may deny an application for a breakwater or
jetty.
e. Repair or reconstruction
of all structures on the subject parcel that are physically destroyed fifty
percent (50%) or more by wind, storm surge, waves or other coastal processes
shall require a new Council Assent.
5. Standards
a. All applicable standards for earthwork in §1.3.1(B) of
this Part shall be met. The base of the seawall, bulkhead, revetment or
toe-of-slope protection for hybrid shoreline protection must be located as
close as practicable to the shoreline feature it is designed to protect.
Nonstructural, hybrid and structural shoreline protection shall be placed
landward of coastal wetlands unless the project is a marsh sill designed for
wave attenuation as part of a marsh creation, enhancement, or restoration
project.
b. The ends of
nonstructural, hybrid and shoreline protection structures shall be tied into
adjacent structures. Where there are no adjacent structures, the new structure
shall gradually return to the slope of the feature and be so designed to
minimize erosion around the back of the structure.
c. For a practice to be considered hybrid
shoreline protection, stone may only be used for toe-of-slope protection or
intertidal sill creation. For the purposes of this section, toe-of-slope
protection shall not extend more than two (2) feet vertically from the bottom
of the bank or scarp along low energy shorelines (i.e., fetch less than 1.5
miles) and four (4) feet vertically from the bottom of the bank or scarp along
high energy shorelines (i.e., fetch greater than 1.5 miles). Stone may be
gathered from the coastal beach directly in front of and no more than
twenty-five (25) feet seaward of the proposed hybrid shoreline protection to be
used for toe-of-slope protection or intertidal sill construction. However, no
materials may be gathered seaward of the mean high water elevation.
d. All anchoring and connecting components of
non-structural, hybrid and structural shoreline protection shall be clearly
shown on site plans. All anchoring and connecting components shall be removed
upon exposure unless being repaired or replaced as part of CRMC approved
maintenance.
e. The base of all
shoreline protection built on unconsolidated sediments shall extend to a depth
equivalent to mean low water or to an appropriate depth as determined by the
methods detailed in the most recent version of the U.S. Army Corps of Engineers
Coastal Engineering Manual. Where practicable, the base shall extend to a depth
of three (3) feet below the area of disturbance.
f. To promote good drainage behind seawalls
and bulkheads, and to minimize the flow of sediment into waterways and avoid
the loss of backfill, all backfill must contain less than ten percent (10%)
silt. If sediment in the area is fine grained, a filtering layer shall be
placed behind and/or beneath the structure, consisting of suitably graded stone
or rock chips or geotextile filter fabric. Weep holes shall be provided for
drainage in sea walls and bulkheads. The use of grout or concrete within,
behind, or over revetments is not permitted.
g. Where feasible, the areas in back of the
structural shoreline protection shall be level for a distance equivalent to its
height.
h. The slope of revetments
shall not exceed 1:1 and the slope of non-structural and non-structural
components of hybrid shoreline protection and associated soil shall not exceed
2:1.
i. Riprap revetments shall be
constructed of angular stone with a minimum unit weight of 165 lbs./cubic foot
(such as granite). The size of stone shall be dependent upon the site's
exposure to wave energy in accordance with the US Army Corps of Engineers
Coastal Engineering Manual.
j.
Applications for structural shoreline protection shall be designed and stamped
by a registered professional engineer.
k. Applicants for hybrid shoreline
protection, as provided for in §1.3.1(G)(4)(a) of this Part, and include
small-scale toe-of-slope protection as part of a hybrid protection project
shall be designed by an appropriate design professional (e.g., registered
professional engineer, landscape architect or land surveyor).
l. Concrete used for sea wall construction
along the shore and in tidal waters shall be resistant to the sulfate attack of
seawater; Type 2 or Type 5 air entraining Portland cement or an equivalent
shall be used.
m. All shoreline
protection construction activities shall minimize any adverse impact to water
quality such as disturbance of sediment.
n. Applicants shall provide appropriate
on-site lateral shoreline access of a similar type and level to that which will
be impacted by the proposed project. Applicants shall submit a plan detailing
the lateral public access over or around the landward side of the proposed
structure.
o. The seaward extent of
the toe of shoreline protection shall be tied into an existing shoreline
feature (e.g., bluff, revetment, seawall, etc.) within the applicant's property
boundary and depicted on the site plan.
p. All previously required coastal buffer
zones or existing areas of natural vegetation landward of the shoreline
protection structure must be preserved, or replaced where disturbed, and
retained in an undisturbed condition.
q. Where no buffer zone or natural vegetation
exists, an area no less than fifteen (15) feet wide immediately landward of the
shoreline protection structure shall be restored to native, deep-rooted (i.e.,
tree or shrub) vegetation to minimize erosion from upland stormwater flows and
overtopping storm surge.
r. A
twenty-five (25) foot setback shall be maintained between the buffer zone or
natural vegetation and nearby structures, excluding any associated residential
structures as defined in § 1.1.2 of this Part.
6. Maintenance and repair of shoreline
protection
a. The maintenance or repair of
shoreline protection shall not extend beyond one (1) foot seaward of the
existing toe of the structure. In most cases, expansion of the shoreline
protection structure beyond one (1) foot seaward of the existing toe and one
(1) foot vertical above the existing or shoreline protection elevation will be
considered new construction.
b.
Maintenance and repair of existing structural shoreline protection shall be the
minimum that is required to maintain the functional viability or structural
integrity. In the case of riprap revetments, the addition of limited quantities
of riprap armor stone to existing damaged revetments may be allowed as a
maintenance activity provided that no impact to coastal resources or lateral
access results. All maintenance shall be in accordance with the policies and
standards of the Coastal Resources Management Program.
c. In the case of shoreline protection that
has undulating horizontal sections, the sections may be straightened in order
to reduce erosion from the concentration of wave energy, provided the repair
and maintenance of the structure is in accordance with §1.3.1(G) (6)(a) of
this Part.
d. It is required that
seawalls eligible for maintenance and that require replacement, pursuant to
§1.3.1(N) of this Part, be replaced with a riprap revetment, hybrid
shoreline protection or nonstructural shoreline protection. Approved
replacement shoreline protection shall begin at the existing toe of the seawall
(no farther seaward) and extend landward.
e. All maintenance and repair activities
shall minimize any adverse impact to water quality such as disturbance of
sediments.
f. All applicable
standards for earthwork in §1.3.1(B) of this Part shall be met for repair
or maintenance activities.
g. In
low energy environments, all maintenance and repair plans for shoreline
protection shall be to scale, show property boundaries at the shoreline,
provide a reasonable depiction of the mean high water mark and all coastal
features, including the shoreline protection structure to be repaired. The
plans must also provide an accurate depiction of the work proposed to include a
plan view with cross-sections. In certain cases, the CRMC Executive Director
may require the submission of plans certified by a RI-registered professional
engineer.
H.
Energy-related activities and structures
1.
Planning for energy facilities a. Planning policies
(1) For applicable policies and standards
pertaining to offshore renewable energy facilities see Subchapter 05 of this
Chapter (CRMC Rhode Island Ocean Special Area Management Plan).
2. Siting of energy facilities
a. Policies and regulations
(1) Facilities for the processing, transfer
and storage of petroleum products and the production of electrical power
provide services necessary to support and maintain the public welfare and the
state's economy. Such facilities, whether sited in the coastal region or
elsewhere, have a high probability of affecting coastal resources and land uses
because of their large size, environmental and aesthetic impacts, and impacts
on surrounding land uses and broad development patterns.
(2) In order to properly and effectively
discharge legislatively delegated responsibilities related to the location,
construction, alteration and/or operation of energy facilities, including
facilities for the processing, transfer and storage of petroleum products and
the production of electrical power, the Council finds a need to require in all
instances a permit for such location, construction, alteration and/or operation
within the State of Rhode Island where there is a reasonable probability of
conflict with a Council plan or program, or damage to the coastal
environment.
(3) The siting,
construction, alteration and/or operation of petroleum processing, transfer or
storage facilities and power generating facilities within the State of Rhode
Island shall require a Council permit when there is reasonable probability
demonstrated by reliable and probative evidence that the proposal will:
(AA) Conflict with any Council management
plan or program.
(BB) Make any area
unsuitable for any uses or activities to which it is allocated by a Council
Plan or Program, or
(CC)
Significantly damage the environment of the coastal region.
(4) Applicants for energy
facilities must consider the projected impacts of climate change, including but
not limited to projected storm surge, coastal erosion and sea level rise to
these facilities.
(5) Applicants
shall be further required to demonstrate by reliable and probative evidence
that:
(AA) Alternative sites have been
considered and rejected for environmental, economic and/or operational
reasons.
(BB) Construction and/or
operation will be in conformance with all applicable environmental standards,
guidelines and objectives.
(CC)
Siting will not cause secondary developments that are inconsistent with the
State Guide Plan or approved municipal comprehensive plans.
(DD) Operation will not degrade aquifers or
water bodies utilized for public water supply, and
(EE) Adequate procedures for the safe
transport and/or disposal of products, materials and/or wastes hazardous to man
or the coastal environment will be taken, including emergency containment and
cleanup.
(6) Where on
the basis of such evidence and/or demonstrations the Council finds a reasonable
probability of noncompliance with any applicable policy or regulation,
including §1.3.8(B) of this Part, it shall require appropriate
modification of or shall deny the application in question.
(7) Recipients of approved Council permits
shall be required to maintain such records as may be necessary to monitor and
ensure compliance of facility operations with all applicable Policies as set
forth above.
(8) Offshore renewable
energy projects shall comply with the policies and standards in Subchapter 05
of this Chapter (CRMC Rhode Island Ocean Special Area Management
Plan).
3.
Certified verification agent (CVA) requirement for energy-related activities
defined in § 1.1.2 of this Part for which the CRMC has jurisdiction or
requires a permit in accordance with §§ 1.1.4 and 1.3.3 of this Part,
and as required by the CRMC executive director to review projects that are
outside the scope of CRMC staff expertise.
a.
The CVA, as defined in § 1.1.2(A) of this Part, shall have licensed and
qualified professional engineers on staff. The CVA is paid for by the
applicant, but is approved by and reports to the Council.
b. The applicant shall not engage a CVA prior
to Council approval, and the CVA must be approved by the Council prior to
starting construction.
c. The
applicant shall use a CVA to:
(1) Ensure that
the applicant's facilities are designed and constructed in conformance with
accepted engineering practices;
(2)
Ensure that repairs and major modifications are completed in conformance with
accepted engineering practices; and
(3) Provide the Council immediate reports of
all incidents that affect the design and construction of the project.
d. The applicant shall nominate a
CVA for the Council approval and shall submit to the Council a qualification
statement that includes the following:
(1)
Previous experience in third-party verification or experience in the design and
construction, or major modification of energy-related activities;
(2) Technical capabilities of the individual
or the primary staff for the specific project;
(3) Size and type of organization or
corporation;
(4) In-house
availability of, or access to, appropriate technology (including computer
programs, hardware, and testing materials and equipment);
(5) Ability to perform the CVA functions for
the specific project considering current commitments;
(6) Previous experience with the Council
requirements and procedures, if any; and
(7) The level of work to be performed by the
CVA.
e. Individuals or
organizations acting as CVAs shall not function in any capacity that shall
create a conflict of interest, or the appearance of a conflict of
interest.
f. The verification shall
be conducted by or under the direct supervision of registered professional
engineers.
g. The applicant shall
nominate a new CVA for the Council approval if the previously approved CVA:
(1) Is no longer able to serve in a CVA
capacity for the project; or
(2) No
longer meets the requirements for a CVA set forth in this subpart.
h. The CVA shall conduct an
independent assessment of all proposed:
(1)
Operational requirements;
(2)
Environmental loading data;
(3)
Stress analyses;
(4) Material
designations;
(5) Soil and
foundation conditions;
(6) Safety
factors; and
(7) Other pertinent
parameters of the proposed design.
i. The CVA shall do all of the following:
(1) Use good engineering judgment and
practice in conducting an independent assessment of the construction of the
facility;
(2) Monitor the
construction of the facility with periodic site inspections to ensure that it
has been built and installed according to the facility design;
(3) Make periodic onsite inspections while
construction is in progress; and
(4) Certify in a report that the facility is
constructed in accordance with accepted engineering practices.
(AA) The certification report shall also
identify the location of all records pertaining to design and
construction.
(BB) The applicant
may commence commercial operations or other approved activities thirty (30)
days after the Council receives that certification report, unless the Council
notifies the applicant within that time period of its objections to the
certification report.
j. If the CVA finds that design and
construction procedures have been changed or design specifications have been
modified, the CVA shall inform the applicant and the Council.
k. The CVA shall make periodic onsite
inspections while construction of the facility is in progress and shall verify
the following items, as appropriate:
(1)
Quality control by builder;
(2)
Material quality and identification methods;
(3) Adherence to structural tolerances
specified;
(4) Nondestructive
examination requirements and evaluation results of the specified
examinations;
(5) Destructive
testing requirements and results;
(6) Repair procedures;
(7) Status of quality-control records at
various stages of construction.
l. The CVA shall spot-check the equipment,
procedures, and recordkeeping as necessary to determine compliance with the
applicable documents incorporated by reference and the regulations under
§1.3.1(H)(3) of this Part.
m.
The CVA shall prepare and submit to the applicant and the Council all reports
required by §1.3.1(H)(3) of this Part. The CVA shall also submit interim
reports to the applicant and the Council, as requested by the Council. The CVA
shall submit one (1) electronic copy and four (4) paper copies of each final
report to the Council. In each report, the CVA shall:
(1) Give details of how, by whom, and when
the CVA activities were conducted;
(2) Describe the CVA's activities during the
verification process;
(3) Summarize
the CVA's findings; and
(4) Provide
any additional comments that the CVA deems necessary.
n. The applicant shall compile, retain, and
make available to the Council representatives, all of the following:
(1) The as-built drawings;
(2) The design assumptions and
analyses;
(3) A summary of the
design and construction examination records;
(4) Results from the required inspections and
assessments;
(5) Records of repairs
not covered in the inspection report submitted.
o. The applicant shall record and retain the
original material test results of all primary structural materials during all
stages of construction. Primary material is material that, should it fail,
would lead to a significant reduction in facility safety, structural
reliability, or operating capabilities.
p. The applicant shall provide the Council
with the location of these records in the certification statement.
q. The Council may hire its own CVA agent to
review the work of the applicants CVA. The applicant shall be responsible for
the cost of the Council's CVA. The Council's CVA shall perform those duties as
assigned by the Council.
4. Prerequisites
a. Applicants must demonstrate that all relevant local zoning
ordinances, building codes, flood hazard standards, and all state safety codes,
fire codes, and environmental requirements have or will be
met.
5. Prohibitions
a. Industrial operations and structures are
prohibited in Type 1 and 2 waters or on shoreline features and their contiguous
areas abutting these waters.
6. Additional Category B requirements
a. Unless preempted under the regulations of
the Federal Energy Regulatory Commission the following summary defines the
scope of the topics that shall be addressed by applicants for power generating
and petroleum processing and storage as they apply to construction, operation,
decommissioning, and waste disposal:
(1)
Environmental impacts,
(2) Social
impacts,
(3) Economic
impacts,
(4) Alternative
sites,
(5) Alternative means to
fulfill the need for the facility,
(6) Demonstration of need, and
(7) Consistency with state and national
energy policies.
b.
Shore front sites shall demonstrate the need for access to navigable waters or
cooling and/or process water.
c.
The above requirements for energy facilities do not have to be addressed if the
proposal is for an electrical generating facility of forty (40) megawatt
capacity or less, or for a petroleum storage facility of less than two thousand
four hundred (2,400) barrel capacity. Such small-scale facilities shall be
considered commercial or residential structures (see §1.3.1(C) of this
Part).
7. Standards
a. See standards given in "Filling, removing,
or grading" in §1.3.1(B) of this Part, as applicable.
b. See standards given in "Residential,
commercial, industrial, and public recreational structures" in §1.3.1(C)
of this Part, as applicable.
c. See
standards given in "Treatment of sewage and stormwater" in §1.3.1(F) of
this Part, as applicable.
8. Transfer of petroleum products
a. Policies and regulations for
transportation by vessel
(1) All vessels
engaged in the transportation of petroleum products in the waters of the state
shall comply with all applicable federal, state, and local laws and
regulations.
(2) It shall be the
adopted policy of the Council to support the Coast Guard in the following
actions:
(AA) Implementation of an oil spill
contingency plan for southern New England in cooperation with appropriate
bodies in other states.
(BB)
Re-evaluation and upgrading of vessel design standards especially as these
relate to the prevention and/or mitigation of accidental spills of petroleum
products.
(CC) Re-evaluation and
upgrading of operational rules relating to transport of petroleum products in
near shore waters and coastal embankments.
(DD) Formulation of standards for crew
training and qualification of all vessels including barges utilized in the
transport of petroleum products.
(3) The storage of liquefied natural gas
(LNG) and liquefied petroleum gas (LPG) may have impacts to Rhode Island's
coastal resources and use, and the Council will evaluate and weigh these
impacts.
b. Policies and
regulations for transfer via pipeline:
(1) The
siting and construction of any pipeline in or across the land and/or tidal
water bodies of the Rhode Island coastal region shall require a Council
permit.
(2) Applicants for such a
permit shall demonstrate by a fair preponderance of evidence that the proposed
action will not:
(AA) Conflict with any
Council management plan or program;
(BB) Make any area unsuitable for any uses or
activities to which it is allocated by a Council management plan or program,
or
(CC) Significantly damage the
environment of the coastal region.
(3) In addition to those requirements set
forth in §1.3.1(H)(2) of this Part, it shall be further demonstrated by
reliable and probative evidence that the coastal resources are capable of
supporting the proposed activity including the impacts and/or effects related
to:
(AA) Scheduling and duration of
construction relative to recreational, wildlife and fisheries use of affected
areas;
(BB) The degree and nature,
if any, of site reclamation proposed; and
(CC) Exposure of the proposed pipelines to
hazardous bottom conditions.
c. Policies and regulations for vessel to
vessel transfer
(1) Transfer operations for
petroleum and petroleum products. Pre-transfer conference: No person shall
commence or cause to be commenced or consent to the commencements of bulk oil
transfer operations unless the following items have been reviewed, agreed upon,
and compiled with by personnel of the vessels involved.
(AA) A licensed officer or certified tanker
man who has full knowledge of the vessel's tanks and cargo handling system
shall be in charge of cargo handling for each vessel receiving or discharging
oil at all times;
(BB) A sufficient
number of adequately trained men shall be assigned to be constantly on duty on
the vessels during cargo transfer operations, to keep the transfer operation
under constant observation to insure immediate action in case of a
malfunction;
(CC) Cargo sequence
for loading or discharging products and the proper baseline for each product
has been established;
(DD) The
handling rate at which oil will be transferred has been established. Reduced
rates are required when commencing transfer, changing the lineup, topping off
tanks or nearing completion of transfer;
(EE) The amount of time to be given when the
off loading vessel desires to start, stop, or change the rate of flow has been
determined;
(FF) A positive
communication and signal system shall be operable during all transfer
operations;
(GG) The emergency
procedures to be followed in order to stop and contain any discharge shall have
been established; and
(HH)
Personnel responsible for transfer shall be clearly identifiable at all times;
prior to transfer operations, personnel responsible for transfer shall be made
known to each other.
(2)
Transfer procedures: No person shall transfer or cause to be transferred or
consent to the transfer of any oil from any oil carrying vessel to any other
oil carrying vessel unless:
(AA) All equipment
through which oil may pass during transfer operations has been inspected
visually prior to each operation. Any hose used in the transfer shall be
pressure tested annually and shall not be subjected to transfer pressures
greater than 75 percent of the last pressure test or greater than the rated
hose pressure, whichever is less. All hoses used in the transfer of petroleum
products from vessel to vessel shall be marked with a hose number. These
markings shall be in color sharply contrasting with the color of the hose and
shall be not less than one and one half (1 1/2) inches high. The operator shall
keep a log book of all tests conducted on the individual hoses. This log book
shall contain the hose number, the test pressure, the date of test, the place
of test, and the signature of the person conducting the test. This log book
shall be available for inspection by a representative of the Coastal Resources
Management Council;
(BB) Hoses are
supported so as to avoid crushing or excessive strain. Flanges, joints and
hoses shall be checked visually for cracks and wet spots;
(CC) Hose handling rigs are of a type which
allows adjustments for vessel movement and hoses shall be long enough so that
they will not be strained by any movement of the vessels;
(DD) Hose ends are blanked tightly when hoses
are moved into position to be connected, and also immediately after they are
disconnected and drained into a drip pan;
(EE) Hoses are not permitted to chafe on
vessels or to be in contact with hot surfaces such as stream pipes or to be
exposed to other corrosive sources;
(FF) Mooring lines and lines securing the
vessels to each other are tended to prevent excessive movement of the vessels;
and
(GG) The surrounding water
shall be inspected frequently during transfer operations. A log of all such
inspections shall be kept and signed by the person making the inspection and
shall be available for inspection by a representative of the Coastal Resources
Management Council.
(3)
Vessel to vessel transfer: Off-loading requirements: No person shall transfer
or cause to be transferred or consent to the transfer of any bulk oil from any
oil carrying vessel to any other oil carrying vessel unless:
(AA) Sea valves connected to the cargo piping
and stern loading connections are tightly closed and sealed with a numbered
seal which is to be logged in the ship's log book;
(BB) The licensed officer on duty must see
that all valves and lines in the pump room are properly lined up for discharge.
An additional check must be made for the same purpose each time the setting is
changed;
(CC) Full rate of
discharge is not attained until lines of receiving vessel are proven clear;
and
(DD) Upon completion of
transfer operations, hoses or other connecting devices shall be vented, blown
down, or sucked out to drain the remaining oil. A drip pan shall be in place
when breaking a connection and the end of the hose or other connecting devices
shall be blanked off before being moved.
(4) Vessel to vessel transfer: Receiving
requirements: No person shall transfer, or cause to be transferred, or consent
to the transfer of any bulk oil from any oil carrying vessel to any other oil
carrying vessel unless:
(AA) All sea valves
connected to the cargo piping, stern discharge and ballast discharge valves are
closed and sealed with a numbered seal which is to be logged in the ship's log
book or some other book or record kept aboard said vessel and available for
inspection;
(BB) Special attention
is paid during the topping off process to the loading rate, the number of tanks
open, the danger of air pockets and the inspection of tanks already loading.
Notice of the slowdown for topping must be given to offloading vessel
personnel; and
(CC) Upon completion
of loading, all tank valves and loading valves are closed. After draining,
hoses shall be disconnected and hose risers blanked.
(5) Vessel transfers while at anchor: No
vessel while at anchor shall transfer petroleum products while gale warnings
(wind velocity thirty-five (35) knots or more) are in effect. Vessel to vessel
transfers may only be carried on in anchorage areas designated by the Coastal
Resources Management Council. The transfer of fuel for a vessel's own use may
take place outside the designated anchorage area, but in no case during gale
warnings.
(6) Spillage during
transfer: Transfer shall cease if a discharge of oil to the waters of the State
occurs during such transfer. Transfer may be resumed when in the judgment of
the Coastal Resources Management Council's representative, after consultation,
if necessary, with the United States Coast Guard or local authority, adequate
steps have been taken to control the spill and to prevent further
spillage.
(7) Scuppers: No person
shall transfer or cause to be transferred or consent to the transfer of any
bulk oil from one oil carrying vessel to another oil carrying vessel unless the
scuppers of any such vessel are plugged watertight during the oil transfer.
However, it will be permissible to remove scupper plugs as necessary to allow
runoff of water provided a vessel crew member stands watch to re-close the
scuppers in case of an oil spill.
(8) Illumination: No person shall transfer or
cause to be transferred or consent to the transfer of any bulk oil after dark
from one oil carrying vessel to another oil carrying vessel unless both vessels
are adequately illuminated.
(9)
Open hatch transfer: Transfer of oil by means of a hose through an open hatch
is prohibited. An exception will be made only when an emergency arises, and
this is the only means of moving flammable oil from one vessel compartment to
another, or of unloading the vessel for the purpose of reducing or preventing
pollution, or for preventing foundering and then only when all possible
precautions to prevent discharge to the waters of the state have been
taken.
(10) Sample collection: No
person shall transfer in bulk nor cause to be transferred from any vessel to
another vessel any petroleum product known as residual lube oils or middle
distillate fuel until they have taken or cause to be taken a composite sample
of such product of not less than one pint from such vessel. Such sample shall
be labeled in a fashion prescribed by the Coastal Resources Management Council
and retained by said person for use by the Coastal Resources Management Council
for a period of not less than sixty (60) days.
(11) Reports and notification. The Council
shall be notified at least twelve (12) hours in advance of any transfer of bulk
oil from one vessel to another. Should unusual circumstances make it impossible
to provide twelve (12) hour notice, the operator shall notify the Council as
soon as possible. Notification is not required for transfer of oil for a
vessel's own use. The report shall include:
(AA) Names of vessels;
(BB) Approximate amount of oil to be
transferred;
(CC) Product type;
and
(DD) Expected time and date of
vessels arrivals.
(12)
Oil spill reporting procedure: In the event of any overboard discharge during
vessel to vessel transfer, the person, firm or corporation responsible for the
discharge shall immediately undertake to remove such discharge. Responsibility
for removal shall remain with the person, firm or corporation responsible for
the illegal discharge. For this purpose, the owner shall have readily available
adequate essential equipment approved by the Council for the containment and
removal of such a discharge, sufficient personnel to deploy and the use of such
equipment. In addition to the existing procedures, the following actions are
necessary. An initial telephone report of any discharge to the waters of the
State shall be made to the Council or Council's representative as soon as
practicable but within two (2) hours. The report shall include:
(AA) Time of discharge;
(BB) Location of discharge;
(CC) Type and amount of oil;
(DD) Assistance required;
(EE) Name and telephone number of person
making report;
(FF) Other pertinent
information; and
(GG) A telephone
report shall also be made to the National Response Center at
1-800-424-8802.
(13)
Second telephone report: A second telephone report shall be made as soon as
adequate information is available but not more than eight (8) hours after the
first report. The report shall include:
(AA)
Success of containment procedures;
(BB) Actions for removal and success of
removal;
(CC) Estimate of area
affected by such discharge;
(DD)
Assistance required; and
(EE) Other
pertinent information.
(14) After removal of such discharge has been
completed, the operator shall prepare a complete written report of the
occurrence and submit such a report to the Coastal Resources Management Council
within ten (10) days. If circumstances make a complete report impossible, a
partial report shall be submitted. This report shall include, but not be
limited to, the following information:
(AA)
Date, time and place of discharge;
(BB) Name of permittee, name of owner of
vessel or other party(ies) involved;
(CC) Amount and type of oil
discharged;
(DD) Complete
description of containment and removal operation including costs of these
operations;
(EE) Complete
description of circumstances causing discharge;
(FF) Description and estimate of third-party
damages;
(GG) Procedures, methods
and precautions instituted to prevent a similar occurrence from
re-occurring;
(HH) Recommendations
to the Coastal Resources Management Council for changes in regulations or
operating procedures;
(II) Name and
address of any person, firm or corporation suffering damages from the discharge
and an estimate of the cost of such damages; and
(JJ) Council telephone number: The Coastal
Resources Management Council is available by calling 401-783-3370, or fax
number 401-783-3767.
(15) Transfer permit: No person as defined in
this section shall transfer or cause to be transferred or consent to the
transfer of any oil from one vessel to another, unless said person holds a
valid permit issued by the Coastal Resources Management Council and is abiding
by all the conditions set forth in these regulations. Said permit shall be
requested on such form as the Council shall from time to time so designate and
shall contain such information as the Council shall deem necessary. Upon
presentation of the completed request for a permit and the payment of the fee
per discharge as identified in Part 10-00-1 of this Title (CRMC Management
Procedures), the Council is authorized to issue a valid permit.
(16) Declaration of inspection: A copy of the
"Declaration of Inspection" required by the United States Coast Guard shall be
in the possession of the operator or his representative and shall be available
to the Coastal Resources Management Council representative who shall, on
demand, be given the opportunity to satisfy himself that the condition of the
vessel is as stated in the "Declaration of Inspection."
(17) Declaration of understanding: A copy of
the "Declaration of Understanding" shall be presented by the vessel's pilot to
the master of the vessel when the former boards the vessel. No transfer of oil
shall be undertaken until such time as the master of the vessel returns the
signed "Declaration of Understanding" to the pilot who shall within five (5)
days deliver said "Declaration" to the office of Coastal Resources Management
Council. Said "Declaration" shall state that the master of the vessel is
knowledgeable of these regulations and agrees to abide by same, and that,
further, such transfer shall be supervised by a person competent in the
transfer of petroleum products from one vessel to another.
(18) Other: Operators shall also complete
such other forms, check lists and reports as the Council from time to time may
require.
(19) Bunkering and
lightering: Nothing in the foregoing regulations should be construed as to
prohibit the function of bunkering vessels or when a demonstrated need is
shown, the lightering of vessels at a place other than the area designated in
these regulations. Such demonstrated need should be evaluated by the Council
who is authorized to set temporary regulations for such procedures.
(20) Designated anchorage areas: The area
designated in Narragansett Bay East Passage for vessel-to-vessel transfer of
oil is that area south of Gould Island and north of the Newport Bridge bounded
by the following coordinates:
(AA) Latitude:
41° 30' 41" North; Longitude: 71° 20' 57" West;
(BB) Latitude: 41° 31' 17" North;
Longitude 71° 20' 29" West;
(CC) Latitude: 41° 31' 42" North;
Longitude: 71° 21' 05" West; and
(DD) Latitude: 41° 30' 49" North;
Longitude: 71° 21' 14" West
d. Policies and regulations for vessel to
shore transfer:
(1) No person shall transfer
nor cause to be transferred from any vessel to a shore installation, any
petroleum product known as residual, lube oils or middle distillate fuel until
they have taken or cause to be taken a composite sample of such product of not
less than one (1) pint from such vessel. Such sample shall be labeled in a
fashion prescribed by the Coastal Resources Management Council and retained by
said person for use by the Coastal Resources Management Council for a period of
not less than sixty (60) days.
(2)
Further, subsequent to the shore transfer of such petroleum product from a
vessel to a shore installation, the operator of such shore installation shall
obtain or cause to be obtained a shore tank composite sample of such product so
transferred and such sample be labeled in a fashion prescribed by Coastal
Resources Management Council, and retained by said person for use by the
Coastal Resources Management Council for a period of not less than sixty (60)
days.
e. Policies and
regulations for petroleum bulk storage:
(1)
The Council finds that shore-front siting of petroleum bulk storage facilities
within the confines of existing tank farms is an acceptable use of the state's
coastal zone.
(2) The Council shall
require permits for such bulk storage facilities and shall require applicants
for such permits to meet all evidentiary burdens set forth under the
requirements in §1.3.1(H)(2) of this Part.
(3) Applicants for petroleum bulk storage
facilities must consider the projected impacts of climate change, including but
not limited to projected storm surge, coastal erosion and sea level rise to
these facilities.
(4) Unless there
is a demonstrated need, the Council shall not permit expansion of existing tank
farms beyond their present bounds, nor shall it permit construction of new
petroleum bulk storage facilities in the coastal region.
f. Policies and regulations for the storage
and processing of liquefied gases:
(1) The
Federal Energy Regulatory Commission (FERC) regulates the natural gas industry
and has responsibility for the regulation of pipeline, storage, and liquefied
natural gas facility siting and construction.
(2) Transfer of liquefied gases from vessels
transporting such gases to bulk storage facilities located in the Rhode Island
coastal region is subject to United States Coast Guard regulations.
(3) The storage of LNG and LPG may have
impacts to Rhode Island's coastal resources and use, and the Council will
evaluate and weigh these impacts.
(4) Siting, construction and operation of
facilities for the transfer, bulk storage or re-gasification of liquefied gases
shall require a Council permit.
(5)
Applicants for such a permit shall be required to meet all permit and
regulatory requirements set forth under §1.3.1(H)(2) of this Part, and to
further demonstrate by a fair preponderance of evidence that facility siting
and operation will be consistent with preservation of the health and safety of
nearby populations.
(6) Applicants
will have to show by a preponderance of evidence that new or expanded LNG or
LPG facilities will not significantly negatively impact existing coastal
resources or uses.
(7) It shall be
further demonstrated by reliable and probative evidence that:
(AA) All applicable federal, state and local
design material and operating regulations, codes or other such requirements
will be complied with;
(BB) Storage
tanks will be constructed of proven materials and will be designed and operated
within the design limits of pressure relief and emergency venting
systems;
(CC) Storage tanks will be
sited at sufficient distance from each other and so isolated by terms or
containments that accidental release and combustion of gases from one cannot
ignite or otherwise damage any other;
(DD) Storage tanks will be sited a sufficient
distance from any stored corrosive material likely to damage or weaken such
tanks. Each tank will be surrounded by a continuous berm or containment of
sufficient diameter and height to contain the entire liquid contents of such
tank;
(EE) Any pipeline for the
transfer of liquefied gas into or from such a facility or on the premises of
such a facility will be provided with dikes or berms capable of containing the
largest spill that might occur if such pipeline was ruptured and before it
could be drained or shutdown;
(FF)
Provision for installation and operation of automatic and continuous
monitoring, alarm and shutdown devices must be made;
(GG) Provision for independent emergency
power to maintain such emergency and essential operating equipment must be
made;
(HH) Provision for fire
protection and firefighting including emergency plans, equipment and personnel
must be made;
(II) Provisions for
spill protection and prevention of ignition must be made; and
(JJ) Provisions must be made for LNG or LPG
terminal security.
(8)
Vaporization of liquid gasses utilizing fresh or marine water sources shall not
be permitted unless such water is recycled. Release of process water to the
coastal environment shall only be permitted upon demonstration that no
significant environmental damage will result.
g. Policies and regulations for the
processing of petroleum products:
(1) Refer to
regulatory requirements in §1.3.1(H)(2) of this Part.
I. Dredging
and dredged material disposal
1. Policies
a. The Council shall support necessary
maintenance dredging activities in Type 2, 3, 4, 5, and 6 waters, provided
environmentally sound disposal locations and procedures are
identified.
b. Where beneficial
re-use options as set forth in R.I. Gen. Laws §
46-6.1-3 are not practical, the
Council favors offshore open-water disposal for large volumes of dredged
materials, providing that environmental impacts are minimized.
c. The Council encourages the use of
innovative near shore methods of dredged materials disposal, particularly when
small volumes of material must be disposed. These options include but are not
limited to the creation of wetlands, shellfish habitat, and beach nourishment
in suitable areas.
d. For disposal
of dredged material resulting from maintenance dredging operations, a Category
A Review may be permitted provided the Executive Director determines that the
disposal is conducted consistent with the RIDEM's dredging regulations and that
the disposal is at an approved disposal facility, or at an approved federal
disposal facility. Category A reviews may also be permitted when:
(1) The upland disposal volume is not greater
than ten thousand (10,000) cubic yards (see §1.3.1(B) of this
Part);
(2) The proposal complies
with all applicable local zoning ordinances;
(3) Applicable soil erosion and sediment
controls are employed (see §1.3.1(B) of this Part); and
(4) The proposal meets the standards of
§1.1.6(E) of this Part.
e. For beach replenishment, a Category A
review may be permitted for the placement of clean sands provided the Executive
Director determines that the placement of the materials shall be for beach
replenishment only, and the proposal meets the standards of
§§1.1.4(E) and 1.3.1(I) of this Part as applicable.
f. The Council utilizes and follows the
prescribed processes outlined in the army corps regulations and manuals for
both upland and in-water dredged material disposal.
g. The Council may require performance
assurance bonds for projects that utilize in-water disposal or transit federal
channels with loaded scows.
2. Prerequisites: R.I. Gen. Laws §
46-6.1-7 specifies that approvals
for dredging and dredged material disposal require Council and DEM approval.
Further, the Council, as the lead agency for dredging, shall be the initial
point of contact for application submittals. The Council and DEM have developed
protocols that set out how proposed dredging activities shall be coordinated
for review. A pre-application consultation request with the Council and DEM
(and other agencies as appropriate) is an element of these protocols and is
strongly encouraged for all applicants.
a.
Permits for maintenance and improvement dredging and disposal projects for
navigational purposes must be obtained from the Army Corps of Engineers as well
as the Council. Council and Army Corps requirements are designed to complement
one another; applicants should consider the requirements of both agencies when
preparing to begin the permit process and may apply for CRMC and Army Corps
permits concurrently.
b. All
materials to be dredged for either open water disposal or upland disposal must
be classified by the Department of Environmental Management (DEM) based upon an
approved analysis process.
c. Any
application for open water disposal of dredged materials shall obtain a
suitability determination from the Army Corps of Engineers.
d. All applicable requirements of the
Freshwater Wetlands Act have or will have been met.
e. Upland disposal of dredged materials must
comply with all applicable local zoning ordinances.
f. When disposal is proposed for approved
upland facilities, the applicant shall provide a letter of acceptance from that
facility, unless the disposal is approved for the central landfill.
g. For dredge volumes greater than ten
thousand (10,000) cubic yards, a pre-application meeting may be required as
determined by the CRMC.
3. Prohibitions
a. The disposal of dredged materials on or adjacent to coastal
wetlands in Type 1 and 2 waters is prohibited unless associated with a
Council-approved program of wetland building or rehabilitation. The disposal of
dredged materials is also prohibited on coastal wetlands designated for
preservation in Type 3, 4, 5, and 6 waters (see §1.2.2(D) of this Part).
b. No dredging for navigational
purposes is permitted in Type 1 waters. Only maintenance dredging may be
permitted in Type 2 waters, except as allowed per §1.2.1(B) of this
Part.
c. It is prohibited to
utilize any mechanical system to remove, relocate, wash or otherwise alter the
seabed in any Rhode Island waters, unless authorized through a council assent.
It is also prohibited to remove, relocate, wash or otherwise alter marine
sediments with any device or deflector without a permit for the specific
equipment, method and location. This regulation is not intended to prohibit or
otherwise impact commercial fishing or shellfishing activities in Rhode Island
waters or to establish additional permitting requirements for such
activities.
4.
Additional Category B requirements
a.
Applicants for all dredging projects shall provide accurate soundings in the
area of the proposed dredging operation.
b. Applicants shall describe any temporary or
permanent disturbance to a coastal feature which is required or anticipated in
order to gain access for heavy equipment to the dredging or disposal
site.
c. When fine-grained
sediments are to be removed, the applicant shall employ proper turbidity
controls as necessary to control the transport of materials placed in
suspension by dredging unless the applicant demonstrates to the Council on the
basis of competent professional analysis that such transport will not be
significant or will be controlled by other measures.
d. The applicant shall limit dredging and
disposal to specific times of the year in order to minimize odors and/or
impacts on fish and shellfish unless the applicant demonstrates to the Council
on the basis of competent professional analysis that such odors or impacts will
not be significant or will be controlled by other measures.
e. Applicants for improvement dredging
projects shall describe, on the basis of competent professional analysis,
anticipated siltation rates, sediment sources, and anticipated maintenance
dredging needs.
f. When dredged
materials are removed from a marine to an upland environment for disposal, the
applicant shall demonstrate that any release of pollutants present in the
materials shall not cause significant environmental degradation.
g. Applicants proposing dredging operations
associated with residential boating facilities in Type 2 waters must
demonstrate that the purpose is to restore channels and basins to dimensions
that support and maintain existing levels of use, and must submit clear and
convincing evidence documenting a diminished use of a facility or navigational
fairway by natural shoaling or accretion, not merely a need for additional
water depth.
5.
Standards: All applications submitted to the Council for dredging and disposal
shall demonstrate that they have met all applicable sections of the CRMC/DEM
dredging application checklist.
a. All
materials to be dredged for either open water disposal or upland disposal must
be classified by the Department of Environmental Management (DEM). Applicants
for dredging or open water disposal of dredged materials shall also be required
to obtain a dredging permit (which contains the Section 401 C lean Water Act
Water Quality Certification) from the DEM.
b. For dredging:
(1) Bottoms of dredged areas shall slope
downward into the waterway so as to maximize tidal flushing.
(2) Bottom slopes at the edges of dredged
areas shall have a maximum slope of fifty percent (50%) percent.
(3) Dredging shall be planned so as to avoid
undermining adjacent shoreline protection facilities and/or coastal
features.
(4) Shellfish dredged
from waters classified SB or lower shall not be made available for human
consumption or bait.
(5) All
dredging at any marina shall be bounded to the footprint of the Marina
Perimeter Limit (MPL). Side slopes associated with such dredging shall be
allowed to extend beyond the MPL and then only when all adjacent structures are
not impacted.
c. For
dredged materials disposal in open water:
(1)
Dredged materials may not be placed in areas determined by the CRMC to be prime
fishing grounds.
(2) Measures must
be employed and described to ensure that all dredged materials will be dumped
solely within the confines of an approved site.
(3) Hydrographic conditions at the approved
disposal site must be such that the disposed dredged materials will remain
within the disposal area and that re-suspension of bottom sediments will be
minimal.
(4) Following disposal
operations involving polluted materials, clean coarse-grained materials may be
required be deposited to cap the spoil mound and minimize the release of any
potential contaminants to the water column. The cap shall have a minimum
thickness of six (6) inches.
(5)
The applicant may be required by the Executive Director to provide for an
environmental monitoring program designed to detail physical conditions and
biological activity at and near the site for a period of at least one (1) year.
The results of such programs shall be made public. This shall not apply to
disposal into the CAD cell. However, if the monitoring of the disposal of
dredged materials at a site is to be performed by, and/or in conjunction with,
a state or federally-sponsored monitoring program, then the applicant shall
adhere to the requirements of such state or federally sponsored
program.
d. For dredged
materials disposal into confined aquatic disposal (CAD) cells:
(1) All scows utilized for disposal of
material into CAD cells shall be bottom dump design and in good working
condition with all seals intact and functional. All scows shall be required to
be inspected and approved by the CRMC prior to undertaking any CAD cell
disposal operation.
(2) No debris
shall be disposed within the CAD cell. All debris generated by dredging
operations shall be removed from all dredge material and legally disposed of in
accordance with state and federal regulations.
(3) The applicant shall have a dredge quality
management (DQM) system installed on the disposal scow. Such system is not
required to be certified by the Army Corps of Engineers, but shall include at a
minimum position, draft, door open and door closed for all dumping operations.
Electronic access shall be available to the CRMC at all times during dredge and
disposal operations. The CRMC shall halt all dredging activities if the scow
and door positions are not working and visible on the DQM interface that was
approved for the project.
(4) All
applicants shall pay the current CAD cell disposal fee established by §
10-00-1.4.6(A)(23) of this Title (CRMC Management Procedures).
(5) Following acceptance by CRMC of the
pre-dredge survey all dumping into the CAD cell shall be at the location(s)
shown on the CRMC dump plan provided to the applicant and contractor. If
disposal occurs outside of the CRMC designated locations dredging may be halted
until a resolution for the misplacement of material is determined.
(6) Any disposal that occurs outside of the
CAD cell limits will result in an immediate halting of dredging operations and
the applicant shall be required to remove improperly dumped material from the
bottom. Such activity will result in the maximum fine available to the CRMC for
each day the improperly dumped material is on the bottom.
e. For dredged materials disposal in the
creation of wetlands, aquatic habitat, or island:
(1) Disposal sites must be in sheltered
environments which are approved by the Council for such purposes and are not
prone to extensive wave or current energies yet subject to sufficient tidal
action to provide adequate flushing.
(2) Dredged materials must be pumped or
placed into a containment area that will permit sediment consolidation and
prevent erosion.
(3) The applicant
must provide for an environmental monitoring program designed to detail
physical conditions and biological activity at and near the site for a period
of at least one year. The results of such a program shall be made
public.
(4) All applicable
requirements of §1.3.1(B) of this Part shall be met.
f. For upland disposal:
(1) Dewatering of dredged materials shall
occur within a properly designed dewatering facility.
(2) After dewatering, dredged materials
placed on uplands adjacent to tidal waters shall be vegetated or otherwise
permanently stabilized. Surface slopes of the disposal area shall be graded so
as to prevent surface ponding.
(3)
Where dredged materials are placed behind a wall or bulkhead:
(AA) The structure shall be suitably
engineered to resist the pressures of the dredged material;
(BB) The material, including fines, shall be
prevented from seeping through the wall or bulkhead by the placement of an
adequate filtering device; and
(CC)
All applicable standards listed for shoreline protection facilities in
§1.3.1(G) of this Part shall be met.
(4) All applicable requirements of
§1.3.1(B) of this Part shall be met.
g. Disposal for beach nourishment:
(1) The placement of dredged materials on a
beach is a preferred disposal alternative, providing that the materials in
question are predominantly clean sands possessing grain size and such other
characteristics to make them compatible with the naturally occurring beach
material.
(2) In areas where the
processes of littoral drift would result in significant re-entry of dredged
sediments into a navigable waterway, dredged materials must be placed on the
down-drift side of the inlet.
(3)
All applicable requirements of §1.3.1(B) of this Part shall be
met.
K.
Aquaculture
1. Policies
a. The CRMC recognizes that commercial
aquaculture is a viable means for supplementing the yields of marine fish and
shellfish food products, and shall support commercial aquaculture in those
locations where it can be accommodated among other uses of Rhode Island waters.
The CRMC recognizes that responsible shellfish aquaculture has a net positive
effect on the environment, and therefore it is permissible in all water types.
As any human activity can have adverse environmental effects, the Council
recognizes the possibility of setting scientifically defensible limits on
aquaculture leasing in any particular water body. The CRMC also recognizes that
in the framework of adaptive management protocols, research into the ecology of
coastal waters and our understanding of ecosystem carrying capacities is
constantly evolving and improving.
b. The Council may grant aquaculture
activities by permit only. The CRMC may grant aquaculture applicants exclusive
use of the submerged lands and water column, including the surface of the
water, when the Council finds such exclusive use is necessary to the effective
conduct of the permitted aquaculture activities. Except to the extent necessary
to permit the effective development of the species of animal or plant life
being cultivated by the Permittee, the public shall be provided with means of
reasonable ingress and egress to and from the area subject to an aquaculture
lease for traditional water activities such as boating, swimming, and fishing.
All plant and animal species listed for culture in an aquaculture lease are the
personal property of the Permittee.
c. At the discretion of the Executive
Director, leaseholders may be required to temporarily remove their aquaculture
facilities, which may include all associated gear and cultured species.
However, the Council may permit aquaculture facilities to remain if it
determines that the temporary removal of these facilities would prove
detrimental to coastal resources of the state. Report of such action by the
Executive Director shall be made to the full Council at the next regularly
scheduled meeting of the Council.
d. The Executive Director may order the
removal of any aquaculture facility that is in an obvious state of disrepair or
has been determined to be a navigation or public safety hazard. Report of such
action by the Executive Director shall be made in writing to the full Council
at the next regularly scheduled meeting of the Council.
e. Upon application to renew an existing
aquaculture Assent, the Executive Director may administratively renew said
Assent for a period not to exceed that period set forth in R.I. Gen. Laws
§
20-10-3 for each renewable period,
provided the applicant is in conformance with the terms and conditions of the
Assent, the aquaculture lease, and with the Coastal Resources Management
Program (RICRMP) in effect at the time of renewal provided, further, that the
applicant is not seeking any amendments or modifications to the Assent or
lease. Report of such action by the Executive Director shall be made in writing
to the full Council at the next regularly scheduled meeting of the
Council.
f. In the event that a
CRMC approved aquaculture operation is determined by the Council to not be
actively farmed for a period of one year, the assent and lease shall be deemed
null and void and the site shall revert to the State's public use upon order by
the CRMC. Actively farmed may be defined by the yearly monetary investment in
the farm (e.g., the purchase of seed and supplies and/or proof of sales). Three
(3) consecutive years of no proof of sales shall be grounds for revocation of
the Assent and lease. The Council may allow the Assent and lease to remain in
effect for inactive aquaculture upon a showing by the Assent holder for good
cause.
g. The Council may grant an
aquaculture Assent for a period not to exceed that period set forth in R.I.
Gen. Laws §
20-10-3.
h. It is the Council's policy to prohibit
private aquaculture activities in not-approved areas as defined by the National
Shellfish Sanitation Program that contain significant shellfish stocks
potentially available for relay into approved areas for free and common
fishery.
(1) This prohibition shall not apply
to the activities of a seed nursery or spat collection, or to the cultivation
of scallops, or to private aquaculture operations conducted within the confines
of a marina perimeter limit (as set forth in §1.3.1(D) of this Part), or
to projects which are designed, with Council approval, to enhance and restore
the public resource.
(2)
Aquaculture projects other than shellfish aquaculture proposed for
conditionally approved waters that are not closed seasonally and prohibited
waters that do not contain significant shellfish stocks potentially available
for relay into approved areas for free and common fishery may be granted by the
Council provided the applicant provides sufficient evidence that no harm to
public health or safety will result. Such activities shall be prohibited unless
the applicant provides a written statement from the director of the department
of health certifying that the proposed activity will not result in product that
is a public health or safety concern.
(3) Authorization may be granted by the
Council for activities prohibited by this subsection provided the operation is
for research purposes or public enhancement of the resource and the applicant
provides written statements from the directors of the departments of
environmental management and health certifying that the proposed activity is
consistent with the requirements of the NSSP.
i. When the Council issues an authorization
for aquaculture all wild shellfish stock, crustaceans, seaweed, and whelks
existing within the authorized area shall remain the property of the
state.
j. Applicants for
aquaculture operations conducted at marinas using technologies such as an
upweller unit may be reviewed as a Category A activity provided that the
operation is conducted within a Council-approved marina perimeter.
k. Upweller units at CRMC permitted
residential docks, piers and floats may be reviewed as a Category A activity
provided that:
(1) Only current
Council-approved aquaculture lease holders may propose to utilize upweller
units at residential docks;
(2) The
inclusion of an upweller is incidental to the permitted use of the dock, pier,
or float, and the original use of the structure not be inhibited by the
inclusion of an upweller;
(3) All
shellfish from the addition of an upweller belong to a licensed CRMC
aquaculture leaseholder and that the production from the upweller will go to
the owner's lease site; and
(4) All
applicable Rhode Island Department of Environmental Management and Rhode Island
Department of Health Regulations are followed.
l. A CRMC assent may be issued for upweller
units at CRMC permitted residential docks for a period of up to five (5) years,
but in no case longer than the length of time remaining on the approved
aquaculture leaseholder's permit.
2. Prerequisites
a. Prior to issuing a permit for marine aquaculture within tidal
waters, the Council shall obtain and give appropriate consideration to written
recommendations from the Director or his or her designee of the Department of
Environmental Management and the chairman of the Marine Fisheries Council, as
required by R.I. Gen. Laws §
20-10-5. The director or his or
her designee of the Department of Environmental Management shall review the
application to determine that the proposed aquaculture activity will not
adversely affect including, but not limited to:
(1) Marine life adjacent to the proposed area
and the waters of the state, and
(2) The continued vitality of indigenous
fisheries.
(AA) The chairman of the Marine
Fisheries Council shall review the application to determine that it is
consistent with competing uses involved with the exploitation of marine
fisheries.
b.
Prior to submitting a formal Category B application to CRMC for aquaculture
activities within tidal waters, applicants must first submit a Preliminary
Determination application for the proposed project. A formal Category B
application may be submitted only after the completed Preliminary Determination
report has been issued by CRMC.
c.
Applicants for aquaculture operations within tidal waters must submit with
their application(s) all required information as specified in the most recent
version of the CRMC aquaculture checklist.
d. At the time of filing a preliminary
determination (PD), the applicant shall include a DRAFT operational plan that
includes the following information:
(1) Name
of the applicant and the company's name;
(2) Contact information for applicant and/or
company;
(3) Description of the
design and activities of the aquaculture facility;
(4) Map depicting the specific location and
boundaries of the aquaculture lease and facility, including the latitude and
longitude points for each boundary point;
(5) Types and locations of structures (rafts,
pens, tanks, etc.);
(6) Species to
be cultured and source of these organisms (i.e., wild or cultured);
(7) Expected level of activity (seasonally,
weekly and daily);
(8) Procedures
to prevent contamination, program of sanitation and maintenance, description of
the water source including details of water treatment, program to maintain
water quality, maintenance of records; and
(9) How shell stock will be harvested.
(AA) The DRAFT operational plan may be
modified during the PD review process and serve as the basis for the
operational plan required below under §1.3.1(K)(3)(b) of this
Part.
e. In
those cases where alterations to freshwater wetlands may occur, applicants for
freshwater and land-based aquaculture operations must first obtain a permit
from the DEM Division of Agriculture or DEM Freshwater Wetlands prior to
applying with the Council.
f.
Applicants for freshwater and land-based aquaculture structures and/or
improvements must obtain local building official approval and zoning approval,
where necessary, prior to submitting an application to the CRMC.
g. Applicants for aquaculture operations
which result in discharges to waters of the state are required to obtain a
Rhode Island Pollution Discharge Elimination System (RIPDES) review by the
department of environmental management to determine if a RIPDES permit is
required. Said permit must be obtained by the applicant prior to any
aquaculture facility discharges to waters of the state.
h. At the time of application, the applicant
must provide an operational plan that details methods and record keeping to
ensure that seed product - prior to exceeding the size of the seed definition -
will be transferred to a permitted aquaculture facility operating in approved
waters, a scientific or educational institution, or a government
agency.
i. Applicants who propose
to introduce non-indigenous species into a CRMC-approved aquaculture facility
or lease are required to design a protocol and submit it for review and
approval by the CRMC and the RIDEM with the advice and consent of the
Bio-Security Board in accordance with R.I. Gen. Laws §
20-10-1.2 prior to issuance of an
assent. This review can occur concurrently with the aquaculture application
process.
j. All freshwater
aquaculture permits will be reviewed by and receive consent from the CRMC
Biosecurity Board prior to issuance of an assent. This review can occur
concurrently with the aquaculture application process.
3. Additional Category B Requirements
a. Applicants proposing to undertake any
aquaculture project shall:
(1) Describe the
location and size of the area proposed;
(2) Identify the species to be managed or
cultivated within the permitted area and over which the applicant shall have
exclusive right;
(3) Describe the
method or manner of management or cultivation to be utilized, including whether
the activities proposed are experimental, commercial, or for personal use;
and
(4) Provide such other
information as may be necessary for the Council to determine:
(AA) The compatibility of the proposal with
other existing and potential uses of the area and areas contiguous to it,
including navigation, recreation, and fisheries;
(BB) The degree of exclusivity required for
aquacultural activities on the proposed site;
(CC) The safety and security of equipment,
including appropriate marking of the equipment and/or lease area;
(DD) The projected per unit area yield of
harvestable product;
(EE) The
cumulative impact of a particular aquaculture proposal in an area, in addition
to other aquaculture operations already in place;
(FF) The capability of the applicant to carry
out the proposed activities; and
(GG) The impact of the proposed activities on
the scenic qualities of the area.
b. Operational plan - In accordance with the
permitting requirements set forth herein, the aquaculturist must submit a
written operational plan as part of their Category B Assent application to be
reviewed and approved by CRMC and DEM and maintained on file with the CRMC.
Operational plans will be made available for review and inspection by CRMC, DEM
and the U.S. Food and Drug Administration. The operational plan must be updated
and resubmitted prior to any change(s) occurring in the aquaculture operation.
Aquaculture must be practiced only in strict compliance with the provisions of
the approved operational plan. At a minimum, each operational plan must include
the following information:
(1) Description of
the design and activities of the aquaculture facility;
(2) Specific location and boundaries of the
aquaculture lease and facility;
(3)
Types and locations of structures (rafts, pens, tanks, etc.);
(4) Species to be cultured and source of
these organisms (i.e., wild or cultured);
(5) Expected level of activity (seasonally,
weekly and daily);
(6) Procedures
to prevent contamination, program of sanitation and maintenance, description of
the water source including details of water treatment, program to maintain
water quality, maintenance of records, and
(7) How shell stock will be
harvested.
4.
Prohibitions
a. Fish pen
aquaculture operations are prohibited in all coastal ponds and nutrient
sensitive shallow embayments and coves.
b. Private aquaculture leases are prohibited
in uncertified waters (i.e., restricted areas as defined by the National
Shellfish Sanitation Program), which contain significant shellfish stocks
available for relay into certified public waters for the free and common
fishery.
c. Upwellers at existing
residential docks, piers, or floats in Type 1 waters are prohibited.
d. Introduction of non-indigenous species is
prohibited unless protocols are in place to ensure that no accidental releases
into the state's waters may occur. These protocols must be submitted by the
applicant for advice and consent by the CRMC Bio-Security Board and approval by
the RIDEM Director before any permit is issued. Any proposed modifications to
the permitted operation will be reviewed by the Bio-Security Board and the
RIDEM Director before an assent modification can be issued. The issuance of a
permit under these stipulations can be revoked if a release of non-indigenous
species takes place during the term of the assent.
e. The harvest of wild bivalve molluscan
shellfish, other than spat collection, naturally occurring in a CRMC permitted
lease is prohibited. All wild shellfish within a lease area will remain the
property of the State of Rhode Island and remain in place for the benefit of
the public resource. This resource is not to be harvested by any person for
commercial or recreational purposes. Any incidental catch by the lease holder
within an aquaculture lease shall be returned immediately to the same
waters.
f. In the coastal salt
ponds, the area occupied by commercial aquaculture, shall not exceed five
percent (5%) of the total open water surface area of the coastal pond below
MLW.
g. Proposed aquaculture leases
may not be sited where eelgrass (Zostera marina) or widgeon grass (Ruppia
maritima) exists.
5.
Standards
a. Marine aquaculture within tidal
waters;
(1) In the event of revocation or
termination of an Assent by order of the Council or expiration of any lease or
Assent, the lessee or Assent holder is responsible for restoring the area to
pre-existing conditions within ninety (90) days from the date of permit
revocation, termination, or expiration. This shall include the removal of all
structures, rafts, floats, markers, buoys, anchors, and other equipment brought
to the site. Failure to comply with the Council's order to restore the site may
result in the removal of gear and forfeiture of the assent bond posted by the
lessee.
(2) Any person who
maliciously and willfully destroys, vandalizes, or otherwise disrupts
aquaculture activities permitted by the Council shall be in violation of an
order of the Council and libel to all fines and penalties under law.
(3) All Permittees shall mark off the areas
under permit by appropriate buoys or stakes, as determined by the CRMC, so as
not to interfere unnecessarily with navigation and other traditional uses of
the water surface. The requirement for the agreed upon marking will be found in
the lease requirements detailed in the assent. All authorized limitations upon
the use by the public of areas subject to the permit shall be posted by the
Permittee.
(4) The aquaculturist
must notify CRMC of every shipment of aquatic plants and animals for culture
entering this state at least five (5) working days prior to entry into the
state and each shipment must be accompanied by a certificate of disease
inspection from a recognized laboratory appropriate to the species received. A
copy of the certificate of disease inspection must be provided to the CRMC.
Prior to shipment the CRMC shall notify DEM Enforcement and DEM Division of
Fish & Wildlife of the shipment.
(5) Shellfish seed cultured in prohibited or
conditionally approved waters may be transferred, by the aquaculturist, to an
approved aquaculture lease in Approved waters in accordance with the terms of
an approved operational plan, and with notification to CRMC. If more than ten
percent (10%) of the cultured shellfish within a lot or batch exceed the
definition of seed (any quahogs that exceed 20 mm, and any oysters that exceed
32 mm), they cannot be moved from other than approved waters to an approved
growing area without prior permission of the DEM Director and the Department of
Health.
(6) All aquaculturists
desiring to use seed that have been cultured in prohibited or conditionally
approved waters must include in the operational plan to CRMC details on how
he/she intends to track and document the growth and harvest of these shellfish.
All aquaculturists must maintain accurate and complete records of all shellfish
seed culture in prohibited or conditionally approved waters and removal of such
shellfish seed to approved waters including, but not limited to, source,
numbers transferred, size composition, time/dates of transfer, harvest and sale
of the shellfish. These records must be maintained for a minimum of two years
and must be available for inspection by agents of the CRMC, DOH, DEM Division
of Law Enforcement, or DEM Division of Fish and Wildlife upon request. If
record keeping and tracking protocols are inadequate, then the aquaculturist
must only use seed from approved waters. No shellfish may be harvested until
they have spent at least six (6) months in approved waters.
(7) Any permitted aquaculturist shall only
harvest those species from the lease area as specifically authorized by the
CRMC Assent.
(8) An aquaculture
license issued by the DEM for the possession, importation, and transportation
of marine shellfish species used in any aquaculture operation shall be obtained
by the applicant from the Director or his or her designee of the Department of
Environmental Management prior to beginning any aquaculture activities. The
aquaculturist, upon receiving the DEM aquaculture license, shall file a copy of
same with the CRMC within thirty (30) days of receipt of said DEM license.
(Note: Any aquaculturist desiring to be a RI shellfish dealer must obtain the
requisite license(s) from DEM and the RI Department of Health.)
(9) The Council may require the leaseholder
for an aquaculture facility to post a performance bond in order to ensure the
cleanup and removal of said facility upon either the termination or expiration
of the lease.
(10) The Executive
Director may approve the transfer of a lease from the lessee to another party
provided the aquaculture operation remains the same, including size, species,
gear, and methods of culturing. The full Council must approve any transfers
that involve a deviation from the existing assented aquaculture
operation.
(11) Permittees must
demonstrate that they are fully utilizing an existing lease area to be eligible
for an expansion as part of a preliminary determination application.
(12) For the area known as upper Narragansett
Bay defined as the area north of latitude of 41 degrees 35 minutes, proposed
aquaculture farms shall be limited to a maximum size of three (3) acres. Leases
may be granted by authorizing an initial two (2) acre lease. Subsequently, the
third acre may be granted when the Permittee demonstrates that the initial two
(2) acre lease is being fully utilized.
(13) Experimental permits.
(AA) The Executive Director may issue an
experimental aquaculture permit for operations which are expressly for the
purpose of developing and testing new gear or techniques for aquaculture
production. Applicants may be approved for three separate sites, with up to an
area of one thousand (1,000) square feet for each site. Experimental sites
shall not be within 500 feet of one another. Areas in excess of this may be
approved by the full Council. Experimental aquaculture Assents shall be valid
for a period not to exceed three (3) years. A lease may be required and the
sale of any aquaculture product is not allowed. Report of such action by the
Executive Director shall be made in writing to the full Council at the next
regularly scheduled meeting of the Council.
(BB) Experimental aquaculture operations
wholly contained within the confines of a council-approved marina perimeter
area excluded from the five hundred (500) foot separation standard, as
contained above, any may maintain a total of three thousand (3,000) square feet
in any configuration for such operations.
(14) Commercial viability permit.
(AA) The Executive Director may issue a
commercial viability aquaculture permit for operations which are expressly for
the purpose of determining if a particular site is suitable for commercial
aquaculture. The applicant may have one site, limited to a thousand (1000)
square feet. Commercial viability permits shall be valid for a period not to
exceed three (3) years. Permits for a commercial viability shall be subject to
a two (2) step process:
(i) Issuance of a
one-time administrative permit for the period of eighteen (18) months; followed
by a one-time council-approved permit for an additional eighteen (18) months. A
lease may be required. Report of such action by the Executive Director shall be
made in writing to the full Council at the next regularly scheduled meeting of
the Council.
(ii) Any continuation
of the operation by the applicant beyond this permit length shall require a
separate application which will be considered and reviewed by the Council as a
Category B application and is subject to all applicable aquaculture policies
and regulations.
(iii) The
permittee may, on a one time basis, sell those products approved within the
permit. Upon termination of the operation, or at the end of the three (3) year
permit period, whichever comes first, the Permittee must terminate the
operation.
(iv) The permittee must
show that, in the case of a successful trial, there is sufficient potential
area to expand to a commercial aquaculture lease in the same area that the
commercial viability permit was granted. The Executive Director may require the
Permittee to post a performance bond in order to ensure the cleanup and removal
of said facility. Detailed economic reports shall be required for all
commercial viability Permittees and included with the annual report that must
be filed with the CRMC.
(15) Education/research permit. The Executive
Director may issue an education/research aquaculture permit for operations
which expressly for the purpose of using aquaculture for education or research.
A lease may be required. Applicants may be approved for three separate sites,
with up to an area of one thousand (1,000) square feet for each site.
Education/research sites shall not be within five hundred (500) feet of one
another. Areas in excess of this may only be approved by the full Council.
Educational/research aquaculture assents shall be valid for a period not to
exceed three (3) years. A lease may be required and sale of any aquacultured
product is not allowed, report of such action by the Executive Director shall
be made in writing to the full Council at the next regularly scheduled meeting
of the Council. The Executive Director may grant extensions to these permits.
Each extension shall not exceed three (3) years. Educational/research
aquaculture operations wholly contained within the confines of a
council-approved marina perimeter are excluded from the five hundred (500)-foot
separation standard, as contained above, and may maintain a total of three
thousand (3,000) square feet in any configuration for such
operations.
(16) Aquaculture
operations shall be located at sites and operated in such a manner as to not
obstruct public access to and from tidal waters.
(17) Any new lease in a coastal salt pond
shall be limited in size as follows:
(AA) A
maximum three (3) acres for methods using gear including, but not limited to,
racks, bags, and floating cages; or
(BB) A maximum of ten (10) acres for bottom
planting.
(18)
Leaseholder may not apply for any lease expansion until such time leaseholder
can demonstrate to the CRMC a need for additional area.
(19) Recreational permits. The Executive
Director may grant permits for recreational culture of shellfish by littoral
landowners as follows:
(AA) Recreational
permits shall be limited to a combined total volume of forty-eight (48) cubic
feet;
(BB) This cage(s) shall be
hung from an existing CRMC approved dock in a manner that it will not interfere
with traditional navigation;
(CC)
Recreational permit holders shall follow all existing seed importation
regulations;
(DD) Recreational
permit holders are required to complete a CRMC approved aquaculture educational
program;
(EE) All gear used under
an education permit will be legibly marked with the letters "CRMC" and the CRMC
permit number; and
(FF)
Recreational permits will be only in areas of approved waters as defined by the
National Shellfish Sanitation Program.
(20) The maximum area occupied by aquaculture
leases in the coastal salt ponds is five percent (5%) of the total open water
surface area of the salt pond below MLW. This limit is established based upon
the current knowledge of ecological carrying capacity models.
b. Freshwater
aquaculture
(1) The Council shall require a
permit for all freshwater and land-based aquaculture operations located within
the coastal zone or in inland locations throughout the state.
(2) Permits for land-based aquaculture
operations shall be granted by the CRMC for a term not to exceed fifty (50)
years.
(3) When required, all
species utilized for culture within land-based aquaculture operations must be
approved by the DEM director or his or her designee. The aforementioned
approval must be obtained prior to the Council issuing its assent, however, it
may be concurrently processed with the Council's review.
L. Coastal
wetland mitigation
1. Policies
a. In cases where the Council determines that
a coastal wetland may be altered (see §1.2.2(D) of this Part), or grants a
special exception to a prohibition listed in §1.3.1(L) of this Part, the
Council shall require the mitigation of all impacts to the coastal wetland.
Permanently lost or significantly altered wetlands shall be replaced through
the restoration of an historical wetland or the creation of a new wetland at a
site approved by the Council.
b.
The Council shall not grant any variance to the policies, standards, and
prerequisites set forth in this section.
c. Pursuant to the Council's "no net loss"
policy, the goal and minimum requirements of wetland mitigation projects shall
be the replacement of permanently lost or significantly altered wetlands with
wetlands of equal or greater area and ecological value. Mitigation projects
shall be carried out in accordance with the standards set forth in
§1.3.1(L)(5) of this Part.
d.
Wetlands created or restored for the purposes of replacing permanently lost or
altered coastal wetlands shall be considered wetlands as defined in §
1.1.2 of this Part and subject to the policies contained in
§§1.2.2(D), 1.1.8 and 1.1.10 of this Part.
e. Activities which shall be exempt from
mitigation requirements include, but shall not be limited to; minor
disturbances associated with the approved construction or repair of shoreline
protection facilities in accordance with §1.3.1(G) of this Part, minor
disturbances associated with approved residential docks and walkways
constructed in accordance with standards set forth in §1.3.1(D) of this
Part, insignificant or minor cutting or pruning of vegetation in accordance
with a Council-approved management or restoration plan; and approved mosquito
population control programs. In addition, wetlands created for the purposes of
stormwater management, erosion control, or waste management, in accordance with
§1.3.1(F), shall not be subject to mitigation requirements.
f. Applicants proposing to alter coastal
wetlands shall submit the application and the proposed mitigation plan
concurrently. In cases where an applicant is proposing an alteration to coastal
wetlands prohibited under §1.3.1(L)(4) of this Part, the applicant shall
be required to first meet the burdens of proof contained in § 1.1.8 of
this Part and obtain a special exception. If the applicant obtains a special
exception, or a special exception is not necessary, then the Council shall
consider the merits of the proposed alteration.
g. The Council shall not consider the
mitigation plan in determining whether an assent shall be granted for the
alteration of a coastal wetland, but shall require mitigation as a condition of
the assent. If the Council approves the proposed alteration to a coastal
wetland, then the applicant shall obtain the Council's approval of the
mitigation plan prior to any alteration of the coastal wetland. The issuance of
the assent to alter coastal wetlands subject to mitigation requirements will be
based, in part, upon adequate assurance that required mitigation is feasible
and will occur.
h. To the maximum
extent practicable, mitigation projects shall be carried out prior to, or
concurrent with, the approved alteration of the coastal wetland.
i. To the maximum extent practicable,
mitigation projects shall be carried out on-site. Where no on-site alternative
exists, the Council may consider off-site mitigation within a hydrologically
connected area. In circumstances where an overall benefit to the state is
demonstrated and no onsite alternative exists, the Council may approve
mitigation projects outside the watershed in which the impact, due to the
alteration of a coastal wetland, will occur.
j. In cases where the alteration is
temporary, the disturbed wetland shall be restored, to the satisfaction of the
Council, immediately following the permitted activity.
k. In no case shall monetary compensation be
considered as an acceptable form of mitigation.
l. The Council may consider proposals for
joint mitigation projects, advanced mitigation projects, and other innovative
wetland mitigation approaches, such as mitigation banks, on a case-by-case
basis.
m. The Council recognizes
that successful mitigation projects depend on a number of variables including
the type of wetland restored or created. Accordingly, replacement ratios
contained in §1.3.1(L)(5) of this Part shall be considered minimum
requirements.
n. Recognizing that
restored and created wetlands require a period of time to become established as
functional coastal wetlands, the Council may require the applicant to post a
bond to ensure compliance with the mitigation plan and other Council
stipulations.
o. Any violation of
the approved mitigation plan shall constitute a violation of the assent to
alter the existing coastal wetland.
p. The Council recognizes the nuisance caused
by large breeding populations of mosquitoes in portions of some coastal
wetlands. The Council recognizes that the problem can be effectively controlled
by good wetland management practices that include open marsh water management,
ditch maintenance and, in some cases, the limited use of pesticides.
2. Prerequisites
a. Applicants proposing any alteration to
coastal wetlands prohibited in §1.3.1(L)(3) of this Part shall be required
to obtain a special exception from the Council (see § 1.1.8 of this
Part).
b. Applicants proposing
alterations to coastal wetlands are required to obtain permits from the Army
Corps of Engineers and applicable permits from the Department of Environmental
Management. In some cases, mitigation projects will require additional permits
from the Army Corps of Engineers and the Department of Environmental
Management. Applicants shall consult with these agencies for a determination of
the need for additional permits and obtain any required permits prior to
undertaking any mitigation activities.
c. Mosquito control programs in any coastal
wetland area will be considered only when authorization from the DEM Division
of Fish and Wildlife, the R.I. Mosquito Abatement Board, and the local
municipality has been obtained. Further, applicants should concurrently obtain
a permit from the Army Corps of Engineers. However, in some cases the Council
may require the applicant to first obtain an Army Corps of Engineers
permit.
3. Prohibitions
a. All alterations to coastal wetlands
abutting Type 1 waters are prohibited except for minimal alterations required
for the construction or repair of an approved or pre-existing structural
shoreline protection facility and alterations resulting from approved mosquito
population control programs.
b.
Alterations to coastal wetlands abutting Type 2 waters and coastal wetlands
designated for preservation adjacent to Types 3, 4, 5 and 6 waters are
prohibited except for minor disturbances associated with:
(1) Residential docks approved pursuant to
the standards set forth in §1.3.1(D) of this Part;
(2) Approved construction or repair of
shoreline protection facilities; and
(3) Approved mosquito population control
programs.
c. Alterations
to coastal wetlands which are adjacent to Types 3, 4, 5 and 6 waters and which
are not designated for preservation are prohibited unless:
(1) The alteration is made to accommodate a
designated priority use for that water area;
(2) The applicant has examined all reasonable
alternatives and the Council has determined that the selected alternative is
the most reasonable; and
(3) Only
the minimum alteration necessary to support the priority use is made.
d. The practice of applying broad
spectrum persistent pesticides on any coastal wetland area is
prohibited.
e. Future development
on any mitigation site is prohibited. All alterations to mitigation sites other
than those required to maintain or enhance the restored or created coastal
wetland are prohibited.
4. Additional Category B requirements
a. Applicants shall demonstrate to the
Council's satisfaction that:
(1) The proposed
alteration will accommodate a priority use, as determined by the adjacent water
type;
(2) The alternative selected
is the most reasonable for supporting that priority use; and
(3) The proposed alteration is the minimum
necessary to support that alteration.
b. Any mitigation plan submitted pursuant to
this section shall include, but not be limited to, the following:
(1) A site plan accurately depicting wetlands
which will be altered, the proposed mitigation site, existing buffer zones and
proposed buffer zones;
(2) The
size, in terms of surface area, of wetlands to be altered and of the proposed
mitigation site. Surface areas shall not include buffer zones; however,
alterations to existing buffer zones shall be described;
(3) A description of existing elevations,
soil types, flora species, vegetative densities and habitats in the wetland to
be altered and for the proposed mitigation site;
(4) A description of the hydrology of the
existing wetland site and proposed mitigation site including ground water
levels and, where applicable, tidal and salinity ranges of the site and of
adjacent inundating waters;
(5) A
description of any excavation, grading, filling, etc. to be conducted as part
of the mitigation plan;
(6) A
description of species to be planted or seeded, spacing of plantings and/or the
density of seeding, the source of vegetation to be planted, and the source of
any organic soils to be introduced at the mitigation site;
(7) A schedule for implementation of the
mitigation plan;
(8) Success
criteria, which shall include benchmark dates and minimum survivability rates
for plantings/seedings;
(9) A
monitoring program; and,
(10)
Evidence of financial security.
5. Standards
a. For alterations to coastal wetlands:
(1) Altered coastal wetlands shall be
replaced by wetlands of a similar type (as defined in § 1.1.2 of this
Part) which provide an ecological value equal to or greater than that of the
altered wetland.
(2) The following
ratios of replacement coastal wetland to permanently altered or lost coastal
wetland shall be considered minimum compensation requirements for mitigation
projects:
(AA) 2:1, area of coastal wetland
restored: area permanently altered or lost or
(BB) 2:1, area of coastal wetland created:
area permanently lost or altered.
(3) Specific replacement requirements shall
be determined on a case-by-case basis, taking into account such factors as
size, type and ecological value of the existing coastal wetland, and the
probability of achieving fully functional replacement at the proposed
mitigation site. In no case shall the Council consider mitigation projects
which do not meet these minimum compensation requirements.
(4) Restored and created coastal wetlands
shall be subject to buffer zone and setback requirements.
b. For mosquito population control
(1) Alterations to coastal wetlands
undertaken as part of a mosquito control program shall be minimal and shall
utilize open marsh water management techniques in accordance with the most
recent version of Manual of Methods for Open Marsh Water Management in Rhode
Island (RIDEM).
(2) Wherever
possible, marsh sediments excavated as part of an approved mosquito population
control program shall be placed at the terminal end of a pre-existing mosquito
ditch identified for abandonment. In cases where such a preexisting mosquito
ditch does not exist or is not a feasible sediment disposal site, marsh
sediments shall be disposed of at a suitable upland location.
(3) Ditches shall be no more than twenty-four
(24) inches wide and not less one (1) foot, or more than three (3) feet,
deep.
Q. Wetland walkover
structures
1. Policies
a. The abundance and diversity of plant and
animal life (reference §1.3.1(A)(1)(e) of this Part), overall habitat
values for feeding, nesting and resting cover for wildlife, fish productivity,
and the probability of providing acceptable habitat for rare and sensitive
species of plant and animal life, often improve dramatically as coastal
wetlands increase in size. Further, certain species depend exclusively on large
tracts of uninterrupted salt marsh. Consequently, activities and alterations
which disturb or bisect large tracts of coastal wetland into smaller segments
cause ecological damage commonly referred to as "habitat fragmentation." The
Council recognizes that habitat fragmentation and other disturbances of large
areas of coastal wetland may significantly impact important ecological values,
or may cause the decline, or eventual elimination of certain species of plant
and animal life.
b. It is the
policy of the Council to prohibit wetland walkover structures unless it is
demonstrated that the structure provides the only reasonable access available
to an applicant for access on his/her property for passive recreational
pedestrian purposes, and that the wetland will incur significant environmental
damage from foot traffic. In cases where the Council finds that wetlands will
not incur significant environmental damage from foot-traffic, dependent on
individual site assessments, the Council may deny wetland walkover
structures.
c. Wetland walkover
structures proposed to extend beyond the limit of emergent vegetative wetlands
are considered residential boating facilities as defined at §1.3.1(D) of
this Part.
2.
Prerequisites
a. Wetland walkover structure
applications in Type 2 waters and in coastal wetlands designated for
preservation or restoration shall be considered Category B applications (see
§1.3.1(A) of this Part). Wetland walkover structures in Type 3, 4, 5, and
6 waters shall be considered Category A* applications.
3. Prohibitions
a.
Activities including but not limited to attached decks, docks,
observation platforms, floats, or other similar structures are prohibited on or
adjacent to wetland walkover structures.
b. Wetland walkover structures are prohibited
in Type 1 waters. Wetland walkover structures are prohibited in Type 2 waters
where there are:
(1) Wetlands having ten (10)
acres or more of salt marsh habitat in total area;
(2) Wetlands determined to have high fish and
wildlife habitat value based on staff review; and/or
(3) Wetlands which provide high scenic value
as determined by the Council. Wetland walkover structures greater than one
hundred (100) feet in length are prohibited.
c. Wetland walkover structures are prohibited
from crossing any salt marsh pools, tidal creeks or pannes, open waters of
coastal ponds, or any other open tidal or nontidal waters, excluding freshwater
streams, rivers, and salt marsh mosquito ditches.
d. Wetland walkover structures are prohibited
over wetlands contained within wildlife refuges, state management areas, and
other public properties, unless the structure is to be used by the public and
is determined by the Council to have no significant environmental
impact.
4. Standards
a. Wetland walkover structures crossing
marshes shall be constructed during the winter dormant season, December 1
through March 15.
b. Construction
over wetlands shall be thirty (30) inches in height above the ground (wetland
substrate) surface as measured from the decking of the structure. In certain
cases, to protect wetlands having tall vegetative life forms, and based on
individual site assessments, the Council may require that the structure be
elevated to a maximum height of fifty (50) inches.
c. Maximum width of wetland walkover
structures shall be two and one-half (21/2) feet.
d. Installation of pilings shall be conducted
manually and spaced fifteen (15) feet on center, spanning the wetland if
possible.
e. Deck spacing shall be
one (1) inch minimum using 5/4" decking material, for light
penetration.
f. In order to
minimize the scenic impact of wetland walkover structures, the use of handrails
shall be strictly avoided. Where it is determined a wetland walkover structure
constructed to CRMP height standards without handrails represents a safety
concern, the Council may choose to grant a variance to the height standard
rather than authorize handrails.
g.
Construction materials of wetland walkover structures shall be limited to
timber or recycled timber products, except for timber connection hardware. The
use of creosote as a wood preservative is prohibited.
h. Site plans for wetland walkover structures
shall be drawn to scale, accurately show all property lines and the affected
wetland, accurately describe the type of wetland to be spanned, and include all
necessary construction details. A site plan prepared by a RI-certified
professional engineer or registered land surveyor shall be required for wetland
walkover structures greater than thirty (30) feet in length, and a biologist
may be required to flag the wetland edge.
i. Wetland walkover structures shall be
limited to one (1) per lot of record.
j. See standards in §1.3.1(B) of this
Part - Filling, removing, or grading of shoreline features, as
applicable.
k. Structures shall be
adequately designed and anchored to resist displacement by storm surge and
wind.
R.
Submerged aquatic vegetation and aquatic habitats of particular concern
1. Policies
a. The Council's goal is to preserve, protect
and where possible, restore SAV habitat. In cases where the Council determines
that SAV may be altered or grants a special exception to a prohibition listed
in §1.3.1(R)(2) of this Part, the Council shall require the mitigation of
all impacts to SAV. Such activities requiring mitigation include, but are not
limited to, marina expansions, dredging, filling in tidal waters, construction
of commercial docks and/or structures and any other activity determined by CRMC
that has not significantly or appropriately avoided impacts to SAV. Permanently
lost or significantly altered SAV shall be replaced through the restoration of
an historical SAV habitat or the creation of a new SAV habitat at a site
approved by the Council. The ratio of restoration to loss shall be
2:1.
b. Activities under CRMC
jurisdiction, including residential, commercial, industrial, and public
recreational structures (§1.3.1(A) of this Part), recreational boating
facilities (§1.3.1(D) of this Part), sewage treatment and stormwater
(§1.3.1(F) of this Part), dredging and dredged materials disposal
(§1.3.1(I) of this Part), filling in tidal waters (§1.3.1(J) of this
Part), aquaculture (§1.3.1(K) of this Part), and activities undertaken in
accordance with municipal harbor regulations (§1.3.1(O) of this Part),
shall avoid and minimize impacts to SAV habitat.
c. The Council supports cooperative efforts
to determine the current status and identify trends in the health and abundance
of SAV species in Rhode Island using the best information as it becomes
available.
d. Deep water habitats
include subtidal waters bordering the immediate shoreline where a depth of
three (3) or more meters is typically achieved within one hundred (100) to two
hundred (200) feet seaward of the MLW mark. In these areas, eelgrass is
typically limited to the shoreline fringe. This environmental setting is
typical of the open waters of Narragansett Bay, Block Island and Rhode Island
Sounds. Examples of these areas include the shorelines of Prudence Island,
Jamestown and Block Island.
e.
Shallow water habitats include subtidal waters where a depth of 3 meters is not
attained within 100 - 200 feet of the shoreline and where the average waterbody
depth is generally less than 3 meters. This situation is typical of the salt
ponds and other shallow coastal embayments.
f. The Council shall assess the potential
impacts to SAV and its habitat from proposed activities on a case-by-case
basis. Such impacts may include, but shall not be limited to, the introduction
of excess nutrients, sedimentation, shading, and/or disruption of SAV and SAV
habitats.
g. All impacts to SAV and
SAV habitat shall be avoided where possible and minimized to the extent
practicable. Where the impacts are substantial or cannot be avoided or
minimized, the Council may deny the application. The Council may exercise
greater discretion if the proposed site is adjacent to or includes a
restoration site and/or the site includes the sole source of SAV
habitat.
h. SAV habitats designated
for preservation within the boundaries of the Narragansett Bay National
Estuarine Reserve (NBNERR) are identified on the SAV Habitats Designated for
Preservation in Narragansett Bay maps (January 13, 2000), available for
inspection at the Council's offices. The Narragansett Bay National Estuarine
Research Reserve includes waters extending to the 18-foot depth contour around
Patience Island, the northern half of Prudence Island, portions of the southern
half of Prudence Island and Hope Island. In areas within the NBNERR which are
designated for preservation on the above maps, alterations and activities which
impact the health and abundance of the SAV habitat are prohibited. These maps
serve to identify individual SAV habitats, and are for general reference only;
in all cases precise boundaries shall be determined through a proper survey
conducted in accordance with these guidelines when proposals that could impact
these features are being considered.
i. In tidal waters where applicants propose
activities under §§
1.3. 1(C), (D), (F), (I),
(J), (K), and (O) of this Part, and the Council's staff determines that SAV
habitat is not present, an SAV survey will not be required. When such
activities are proposed in areas of current or historic SAV habitat, an SAV
survey shall be required (see §1.3.1(R)(3) of this Part).
j. It is the policy of the Council that SAV
surveys shall be completed during peak biomass. SAV surveys shall be completed
in Narragansett Bay between July 1 and September 15. SAV surveys shall be
completed in the south shore coastal ponds and other shallow water embayments
between July 1 and August 15. SAV must be avoided where possible by utilizing
any available location and orientation which does not require crossing the bed
with the dock. In evaluating applications for dock construction, and/or
modifications to existing docks, in areas of known SAV habitat, the Council
will consider dock design features including, but not limited to, the height
and width of the dock structure, the orientation of the dock structure, the
availability of sunlight to the eelgrass habitat, the cumulative impacts of
multiple docks in the area, the disruption caused by construction and the
disruption caused by normal use and maintenance of the dock structure. In
determining the permissible design of a facility in an SAV habitat, the Council
will rely on the latest available research, such as research findings developed
by Burdick and Short (1995), and designs appropriate for the area.
k. Aquaculture operations, which utilize
floating racks and bottom culture techniques, can shade SAV. However, shellfish
aquaculture is acknowledged to improve water quality. Therefore, in cases where
an aquaculture permit has been issued where SAV was not present and then due to
improved water quality as a result of aquaculture operations, SAV subsequently
colonizes within the permitted facility area, the leaseholder shall be
considered grandfathered and not subject to the standards/requirements of this
section. Future proposed expansions shall be subject to review under this
section.
2. Prohibitions
a. The Narragansett Bay National Estuarine
Research Reserve (NBNERR) includes waters extending to the eighteen (18) foot
depth contour around Patience Island, the northern half of Prudence Island,
portions of the southern half of Prudence Island, and Hope Island. In areas
within the NBNERR which are designated for preservation on the SAV Habitats
Designated for Preservation in Narragansett Bay maps, alterations and
activities which impact the health and abundance of SAV habitat are
prohibited.
b. Floats, and float
and platform lifts (including grate-type structures) associated with
residential docks are prohibited over SAV as defined herein (See
§1.1.2(A)(157) of this Part).
c. Boat lifts having the capacity to service
vessels larger than a tender (vessels greater than twelve (12) feet long and
greater than one thousand two hundred (1,200) lbs) are prohibited over
SAV.
d. The long-term docking of
vessels at a recreational boating facility shall be prohibited over
SAV.
e. Residential docks that span
eelgrass beds to avoid and/or minimize impacts to said eelgrass and which are
proposed to be 200 feet or more in length seaward of mean low water (MLW) shall
be prohibited.
3.
Standards
a. For activities under
§§1.3.1(C), (D), (F), (I), (J), (K), and (O) of this Part, where the
Council's staff is satisfied that SAV is not present within the limits of the
proposed activity, an SAV survey will not be required.
b. For activities under §§1.3.1(C),
(D), (F), (I), (J), (K), and (O) of this Part, the Council shall require SAV
surveys in tidal waters of the south shore salt ponds and other shallow water
embayments, around Jamestown, Newport and in other areas when the Council's
staff has evidence of SAV habitats. In areas where the Council's Staff lacks
enough evidence to make a determination of SAV presence or absence, an SAV
survey may be required.
c. A survey
that has been conducted three or more years prior to the date of the
application will not satisfy the requirements of this section.
d. Where an SAV survey is required, the
following standards are required. CRMC staff may require additional
information:
(1) SAV surveys shall be
completed during peak biomass. SAV surveys shall be completed in Narragansett
Bay between July 1 and September 15. SAV surveys shall be completed in the
south shore coastal ponds and other shallow water embayments between July 1 and
August 15.
(2) Define the area of
SAV within the limits of the proposed activity. The SAV survey requires a
series of transects located between the property line extensions associated
with the proposed project site. A survey shall include transect lines (quantity
dependent on the size of the project area) running perpendicular to the
shoreline three (3) meters apart (10 feet). Along each transect line a 1m²
quadrat sampling station shall be placed every three (3) meters (10 ft). It is
important to go beyond the impacted area, especially to understand the impacts
of the dock to SAV. In the case of fragmented beds, transect lines every two
(2) meters may be necessary. For projects not adjacent to the shoreline (i.e.,
aquaculture projects), locate the transects relative to another reference, such
as a channel boundary or depth gradient.
(3) Define a datum. The survey data for SAV
shall be mean low water (MLW). MLW shall be set equal to zero.
(4) Quantify SAV along the transects.
Establish in-water sampling stations along transects along the bottom or as
otherwise necessary to accurately delineate the bed. Use a quadrat measuring 1
m on each side. At each sampling station, determine percent coverage for SAV.
Record the following data for each station:
(AA) General sediment type (silt, mud, sand,
shell, etc.) based on observation or shallow surface core only;
(BB) Estimate of percent coverage for each
quadrat; and
(CC) Estimate the mean
shoot length.
(5) Report
data collected. Overlay the SAV percent coverage and water depth data onto the
site plan for the dock. Show transects, sampling stations, water depth, date
and time of survey, and fixed-point locations on the site plan. For each
transect, areas of SAV and associated water depth shall be located on the
plans, as well as the landward and seaward (where practicable) limits of
SAV.
e. Standard design
options for the construction of residential boating facilities in areas of SAV
habitat.
(1) If it is determined that SAV
cannot be avoided, the impact to the bed must be minimized by reducing the
amount of structure over the bed, by making provisions for avoiding the docking
or mooring of boats over the bed and through the utilization of a design which
minimizes boat travel through the bed as necessary to minimize propeller
impacts including leaf shearing and sediment scouring.
(2) Deep-water habitat (see §.
1.3.1(R)(1)(c) of this Part) dock design: Docks which cannot avoid the crossing
of SAV shall minimize shading impacts through the utilization of a design which
is consistent with the "Burdick and Short" method. Docks designed to the
Burdick and Short method shall extend to a minimum depth of - 5' MLW or shall
extend to the seaward limit of the bed. CRMC regulations prohibit the
installation of floats over eelgrass beds (see §1.3.1(R)(4)(b) of this
Part). Facilities which do not span the bed shall terminate as an elevated
fixed pier or may utilize a fixed T or L section which is turned at a 90-degree
angle to the main pier. All fixed T and L sections shall be designed to meet
Burdick and Short. Access from the fixed pier, T or L section shall be by a
ladder. Applicants proposing a dock using this design methodology may not dock
a boat at the facility for purposes other than touch and go use and must show
that a mooring is available for the long-term mooring of vessels proposed to be
serviced by the facility. "Burdick and Short" methodology is available from the
CRMC.
(3) The maximum length for
facilities designed to meet Burdick and Short shall be when a depth of -5 MLW
is obtained.
(4) Where a facility
is not authorized to have a float, boat lifts to service tenders twelve (12)
feet in length or less and having a one thousand two hundred (1,200) pound
weight capacity or less may be authorized. These lifts shall be located near
the terminus of the T or L section and achieve a minimum depth of four (4) feet
MLW. Boat lifts of greater capacities over SAV are prohibited (see
§1.3.1(R)(4)(c) of this Part).
(5) In shallow water habitats, where it is
possible to avoid the bed by limiting the seaward extent of the facility, the
design plans must depict the inland edge of the existing bed as well as depth
soundings along the proposed facility. If a depth of 18 inches at MLW is
obtained prior to encroaching on SAV, then the dock shall terminate at that
length and depth.
(6) Pile driving
equipment may not be grounded on SAV during construction.
f. In order to minimize impact upon SAV, all
operations and docking of vessels shall be confined to the terminal portion of
the facility. Docking and operation of motorized boats and/or other vessels
elsewhere along the facility shall only be permitted over areas of no SAV
habitat, as determined during staff review.