S.C. Code Regs. § 30-12 - Specific Project Standards for Tidelands and Coastal Waters
A. Docks and Piers: A dock or pier is a
structure built over and/or floating on water and is used to provide access to
water and for the mooring of boats. Docks and piers are the most popular method
of gaining access to deep water. Docks and piers sometimes pose navigational
problems, restrict public use of the water and, under certain circumstances,
possess potential for creating environmental problems. This section is divided
in five parts providing standards for 1) all, 2) private and joint use, 3)
master planned, 4) commercial and (5) community docks. Docks are defined in
30-1.D(16) Docks. Community docks have less environmental impact than multiple
private or joint use docks. One or more community dock(s) in a development will
be permitted when sufficient numbers of private or joint use docks are
eliminated and other applicable Department regulations are met. This section
does not include standards for marinas, which are addressed in 30-12.E. Marinas
by definition include docks with more than 250 linear feet of effective docking
space.
(1) The following standards are
applicable for construction of all docks and piers:
(a) Docks and piers shall be limited to one
structure per parcel or lot and in all instances, parcels or lots must be
waterfront as defined by 30-1.D(53), shall not restrict the reasonable
navigation or public use of State lands and waters;
(b) Docks and piers shall be constructed in a
manner that does not restrict water flow;
(c) The size and extension of a dock or pier
must be limited to that which is reasonable for the intended use;
(d) Docks and piers should use the least
environmentally damaging alignment;
(e) All applications for docks and piers
should accurately illustrate the alignment of property boundaries with adjacent
owners and show the distance of the proposed dock from such extended property
boundaries. For the purpose of this section, the extension of these boundaries
will be an extension of the high ground property line. The Department may
consider an alternative alignment if site specific characteristics warrant or
in the case of dock master plans, when appropriate.
(f) Walkways leading to the dock or pier
should be elevated at least three feet above mean high water.
(g) Dry storage in uplands will be encouraged
in preference to moorage in crowded areas;
(h) Developers of subdivisions and multiple
family dwellings are encouraged to develop plans which include joint-use docks
and/or community docks at the time of required dock master plans. Dock
corridors on the approved Dock Master Plan (DMP) must be shown with bearings or
State Plane Coordinates on a recordable subdivision plat for the development,
and recorded in the appropriate County Office of Deeds. Subsequent re-surveys
or modifications to lots shall reference the dock corridors on the recorded
subdivision plat and be submitted to the Department. Reference to this DMP must
be given in all contracts for lot sales.
(i) Project proposals shall include
facilities for the proper handling of litter, waste, refuse and petroleum
products, where applicable;
(j)
Where docks and piers are to be constructed over tidelands utilized for
shellfish culture or other mariculture activity, the Department will consider
rights of the lessee and the public prior to approval or denial.
(k) Docks cannot be enclosed by walls or
screens.
(l) Docks longer than
1,000 feet over critical area are prohibited. This is inclusive of pierheads,
floats, boatlifts, ramps, mooring pilings and other associated
structures.
(m) Handrails, if
proposed, shall be limited to a maximum height of 36"' above the walkway or
pierhead decking.
(n) Docks must
extend to the first navigable creek, within extensions of upland property lines
or corridor lines, that has a defined channel as evidenced by a significant
change in grade with the surrounding marsh; or having an established history of
navigational access or use. Such creeks may only be bridged/crossed when there
are rare geographic circumstances, such as very close proximity of a
significantly larger creek within extensions of property or corridor lines, may
warrant dock extension to a creek other than the first navigable creek. A creek
with an established history of navigational use may also be considered as
navigable. In exceptional cases, the Department may allow an open water channel
to be bridged if current access is prohibited by other man made or natural
restrictions or if site-specific conditions warrant such a crossing.
(o) This section applies to lots subdivided
or resubdivided after May 23, 1993.
(i) To be
eligible for a private or commercial dock, a lot must have:
(a) 75 feet of frontage at the marsh edge,
and
(b) 75 feet between its
extended property lines at the location in the waterbody of the proposed
dock.
(ii) Joint use
docks will be considered for adjacent waterfront properties each of which must
have:
(a) 50 feet of frontage at the marsh
edge, and
(b) 50 feet between its
extended property lines at the location in the waterbody of the proposed
dock.
(iii) To be
eligible for a community dock, a lot must have:
(a) 50 feet of frontage at the marsh edge,
and
(b) 50 feet between its
extended property lines at the location in the waterbody of the proposed
dock.
(iv) Lots less
than 50 feet wide at the marsh edge are not eligible for a dock.
(p) No docks, pierheads or other
associated structures will be permitted closer than 20 feet from extended
property lines with the exception of joint use docks shared by two adjoining
property owners. However, the Department may allow construction closer than 20
feet or over extended property lines where there is no material harm to the
policies of the Act.
(q) If a dock
is destroyed, the dock may be rebuilt to its previous configuration so long as
reconstruction is completed within five years of the date of the event unless
there are extenuating circumstances justifying more time.
(r) In the event that a dock owner intends to
change the use of a dock from the permitted use or non-permitted grandfathered
use, a new permit must be obtained prior to the change in use. The change in
use is based on the types of docks distinguished by these
regulations.
(2) The
following standards in addition to those in R.30-12(A)(1)are applicable for the
construction of private and joint use docks:
(a) Storage on docks will be limited to a
bench-like locker no larger than 3 feet high, by 3 feet deep, by eight feet
long.
(b) Walkways leading to a
dock or pier shall not exceed 4 feet in width. For handicapped access, the
Department may utilize The Americans with Disabilities Act (ADA)
recommendations for walkway width and other structural configurations.
Reference 28 CFR Part 36.
(c) The
Department sets forth the following standards for size and use of pierheads and
floating docks based on creek widths. Total allowable dock square footage as
used in this section includes the areas of any fixed pierheads, floating docks,
the area of boat storage docks, additional areas covered by a roof, and areas
bounded by an unroofed boatlift, davit or similar structure; and excludes
walkways, catwalks, ramps, mooring buoys, and mooring piles. For purposes of
determining creek width, if marsh vegetation does not exist, the Department
will utilize other indicators of channel width such as changes in grade and the
critical area boundary. Lots in subdivisions with approved DMPs as of May 24,
2002, are exempt from R.30-12.A(2)(c)(i) and (ii) as amended on May 24, 2002.
R.30-12.A(2)(c)(i) and (ii) as amended on May 24, 2002, does not apply to lots
of record that existed as of May 24, 2002, until the later of July 1, 2007, or
the expiration of any permit issued prior to that date.
(i) Docks will not be permitted on creeks
less than 10 feet wide as measured from marsh vegetation on each
side.
(ii) Docks will not be
permitted on creeks less than 20 feet wide as measured from marsh vegetation on
each side unless one of the following two special geographic circumstances
exists: a lot has greater than 500 feet of water frontage or no potential
access via dockage from the opposite side of the creek. If special geographic
circumstances exist, total allowable dock square footage will be restricted to
50 square feet. Boat lifts, davits, and boat storage docks will not be
permitted on any dock allowed in creeks less than 20 feet wide.
(iii) On creeks between 20 and 50 feet, as
measured from marsh vegetation on each side, total allowable dock square
footage shall be restricted to 120 square feet unless special geographic
circumstances and land uses warrant a larger structure.
(iv) On creeks between 51 and 150 feet, as
measured from marsh vegetation on each side, total allowable dock square
footage shall be restricted to 160 square feet unless special geographic
circumstances and land uses warrant a larger structure.
(v) On creeks larger than 150 feet, as
measured from marsh vegetation on each side, total allowable dock square
footage shall be restricted to 600 square feet unless special geographic
circumstances and land uses warrant a larger structure;.
(vi) The Department will allow additional
square footage for joint use docks above and beyond the size allowed for
individual docks, not to exceed 2 times that allowed in subsections
R.30-12.A(2)(c)(i) through (v); contingent upon the sharing of the walkway and
pierhead.
(vii) Grandfathered or
previously permitted fixed and floating docks which are larger than allowed in
R.30-12(A)(2)(c)(ii-v) may not be enlarged.
(viii) Enclosed boathouses are
prohibited.
(ix) Boats moored at
docks cannot restrict the reasonable navigation or public use of State lands
and waters. Under no circumstance are live-aboards allowed at private docks.
Commercial activities are prohibited at private docks unless they are
water-dependent and approved by the Department. Illegal use of a private dock
is grounds for permit revocation.
(x) Boat storage structures will not count
against the total dock square footage as outlined in 30-12.A(2)(c)(ii-vi) if
the size of the structure is 8 feet by 20 feet or less. The area of any larger
structure greater than 160 square feet will count against the total allowable
dock square footage.
(d)
Roofs on private docks will be permitted on a case-by-case basis, with
consideration given to the individual merits of each application. Precedent in
the vicinity for similar structures will be considered as well as the potential
for impacting the view of others. Roofs that have the potential to seriously
impact views will not be allowed, while those that have minimal impact may be
allowed. The following standards will be used in evaluating applications for
roofs.
(i) Roofs shall be clearly shown on the
public notice application drawings, and described in the written description of
the project. Attics or enclosed ceiling storage on roofed docks are
prohibited.
(ii) Flat roofs are
prohibited. Where a roof is otherwise permissible, maximum allowable roof
height shall be 12' as measured from the floor decking of the dock to the
highest point of the roof including any ornamental structures.
(iii) Rails on decks are not to be
incorporated into roofs and no steps, ladders or other means of accessing the
roof on a permanent basis are allowed.
(e) Boat storage structures are allowed,
provided the entire docking system is limited to the minimum structure size
needed to accomplish the intended use. The following standards will be used in
evaluating applications for boat storage structures:
(i) Single family docking facilities will be
limited to one boat storage structure per docking facility on creeks between 20
feet and 50 feet; and a maximum of two boat storage structures will be allowed
on creeks wider than 50 feet.
(ii)
Hull scraping, sandblasting, painting, paint removal, and major engine repair
are prohibited on lifts and davits.
(iii) Boatlifts must be open sided with no
enclosures. Catwalks are allowed to provide access on one side and shall be a
maximum of 3 feet wide.
(3) The following procedures in addition to
those in R.30-12(A)(1)will be followed for docks covered by Dock Master Plans
(DMPs):
(a) A permit may be issued for docks
covered by a DMP, as outlined in CH.III.VI.D of the Coastal Zone Management
Plan. This permit for multiple docks must be placed on public notice and
processed as a major application. If a DMP is approved by the Department, but
no permit is applied for or issued, the approved DMP will be used as a
framework for future permitting decisions, subject to comments received during
the public review process.
(b)
Before individual structures covered by the permit are constructed, written
notice must be given to and a construction placard received from the Department
to insure the docks are built according to the plan.
(c) Major modifications of individual
structures that would require a new public notice will not be permitted;
however those modifications that are minor in nature will be considered as long
as the request is in keeping with the spirit of the DMP.
(d) If the permit expires before all of the
docks permitted have been constructed, subsequent permit applications for the
remaining structures will be reviewed for consistency with the DMP unless the
DMP no longer reflects Department policies and regulations.
(e) Extensions of permits for multiple docks
will be issued upon a showing of significant activity under the
permit.
(4) The
following standards in addition to those in R.30-12(A)(1)apply to construction
of commercial docks that are not marinas:
(a)
The size and extension of the dock must be limited to that which is reasonable
for the intended use and the geographic circumstances of the site. However, no
docks will be permitted in creeks less than 20 feet wide as measured from marsh
vegetation on each side.
(b) Each
applicant for a commercial dock must submit an Operations and Maintenance
Manual with the permit application.
(c) New commercial docks are not allowed in
waters classified for shellfish harvesting if their proposed uses would result
in the closure of additional waters for shellfish harvesting.
(d) Commercial docks should be located in
areas that will have minimal adverse impact on wetlands, water quality,
wildlife and marine resources, or other critical habitats.
(e) Where commercial dock construction would
affect shellfish areas, the Department must consider the rights of the lessee,
if applicable, and the public, as well as any possible detrimental impacts on
shellfish resources.
(f) Project
proposals shall include facilities for the proper handling of litter, waste and
other refuse in accordance with DHEC regulations.
(g) Adequate parking for users of the
commercial dock shall be demonstrated.
(h) The criteria for determining roof
construction described in 30-12A(2)c apply to commercial docks.
(5) The following standards in
addition to those in R.30-12(A)(1)apply to construction of community docks that
are not marinas:
(a) The size and extension
of the community dock must be limited to that which is reasonable for the
intended use.
(b) No leasing or
other transfer of space to individuals who do not reside in the community or
other commercial uses are allowed at community docks.
(c) Community docks are strongly encouraged
and will only be permitted in lieu of multiple single-family docks. Eliminating
private docks on small creeks in exchange for permitting of community docks on
larger waterbodies minimizes environmental impacts. If a sufficient number of
private docks are eliminated, the Department will consider permitting more than
one community dock for a subdivision provided no applicable Department
regulations are contravened. The ratio for determining community dock size (or
slip moorage) in exchange for single-family docks will be 2 to 1 or 40 feet of
community dock length for each private dock that is eliminated. If a joint use
dock is eliminated, the number of lots served by the dock will count as the
number of docks eliminated.
(d) No
section of any community dock (pierheads or other associated structures) will
be permitted closer than 20 feet from extended property lines. However, the
Department may allow construction closer than 20 feet or over extended property
lines where there is no material harm to the policies of the Act.
(e) Community docks will be prohibited on
creeks less than 20 feet in width, however on creeks larger than 20 feet the
size of the structure will be determined by the language in 30-12.A(5)(a) as
well as (c).
(f) Walkways leading
to a dock or pier shall not exceed 6 feet in width. For handicapped access, the
Department may utilize The Americans with Disabilities Act (ADA)
recommendations for walkway width and other structural configurations.
Reference 28 CFR Part 36.
B. Boat ramps:
(1) Boat ramps provide access to the water
for those who do not have water access by means of docks, piers, or marinas.
However, boat ramp construction may require filling or, in some cases, dredging
of wetland areas.
(2) Specific
standards which shall apply are as follows:
(a) Filling or excavating of vegetated
wetlands for boat ramp construction is prohibited unless no feasible
alternatives exist in non-vegetated wetland areas. In addition, the area to be
filled or excavated must be limited to that which is reasonable for the
intended use;
(b) Boat ramps must
consist of environmentally acceptable materials, demonstrate sound design and
construction so that they could reasonably be expected to be safe and
effective, and minimize adverse effects.
(c) Justification for boat ramp construction
in environmentally sensitive areas shall be considered using the following
priorities:
(i) Public use - open to all
citizens;
(ii) restricted use -
open to citizens of a particular area or organization only;
(iii) private use - use for one citizen or
family;
(d) In cases
where private use is necessary, siting of ramps must, wherever feasible, be
located in areas where the least environmental impact will accrue to the area
and be limited to 12 feet in width;
(e) Boat ramp location requiring dredging or
filling of wetlands to provide deep water access to the ramp, parking areas for
the ramp, or other associated facilities are prohibited unless no feasible
alternatives exist and environmental impacts can be minimized;
(f) The siting of "public use" boat ramps is
encouraged in easily accessible areas such as bridges and existing, abandoned
causeways, provided that these sites comply with other applicable
regulations.
C. Bulkheads and Revetments (Rip-rap) (Other
than ocean front, as covered under R.30-13(N)):
(1) In an attempt to mitigate certain
environmental losses that can be caused by these structures, the following
standards are adopted:
(a) Structures must be
designed to conform to the critical area line (upland boundary), to the maximum
extent feasible, and constructed so that reflective wave energy does not
destroy stable marine bottoms or constitute a safety hazard;
(b) Structures may be constructed up to 18
inches from the existing escarpment. In situations where this is not feasible,
Department staff will determine the location of the bulkhead or revetment on a
site by site basis;
(c) Bulkheads
and revetments will be prohibited where marshlands are adequately serving as an
erosion buffer, where adjacent property could be detrimentally affected by
erosion or sedimentation, or where public access is adversely affected unless
upland is being lost due to tidally induced erosion.
(d) Bulkheads and revetments will be
prohibited where public access is adversely affected unless no feasible
alternative exists.
D. Cables, Pipelines, and Transmission Lines:
(1) Installation of cables, pipelines, and
transmission lines is preferred in non-wetland areas. Excavating activities in
critical areas are sometimes required with the preferred alternative being
directional boring. Excavation and filling also are sometimes required to
construct foundation structures attendant to the installation of overhead
transmission line crossings. These installations shall be designed to minimize
adverse environmental impacts.
(2)
In addition to standards for dredging and filling, the following standards are
applicable:
(a) To the maximum extent
feasible, alignments must avoid crossing the critical areas;
(b) Creation of permanent open water canals
to install pipelines is prohibited since such projects usually interfere with
drainage patterns and may adversely affect water quality through accelerated
bank erosion;
(c) Dimensions of
temporarily excavated canals for cables and pipelines should be minimal. Silt
curtains are required for all excavations;
(d) Wherever feasible, all excavations in
wetland areas must be backfilled with the excavated material after installation
of the appropriate structure, while being careful to maintain the original
marsh elevation. In addition, excavated material must be stockpiled on
highground whenever feasible;
(e)
Appropriate erosion control measures shall be employed during the crossing of
wetland areas. Where appropriate, revegetation with suitable wetland species
will be required;
(f) Alignments of
new projects should be designed to utilize existing rights-of-way and
topographic features, wherever feasible;
(g) The extension of public services, such as
sewer and water facilities, involving the expenditure of public funds or
issuance of government revenue bonds to previously undeveloped barrier islands
will not be approved unless an overriding public interest can be
demonstrated.
E. Marinas, including commercial and
community docks with more than 250 linear feet of effective docking space.
(1) In addition to standards applicable for
bulkheads and seawalls, dredging and filling, and navigation channels and
access canals, the following standards apply to all structures defined as
marinas in
30-1(D):
(a) Each applicant for a marina must submit
an Operations and Maintenance Manual with the permit application. This
Operations and Maintenance Manual must be in accordance with 30-12(E)(3), and
approved in writing by the Department staff. The requirements for the
Operations and Maintenance Manual may be modified if deemed necessary by the
Department.
(b) All marinas affect
aquatic habitats to some degree, but adverse effects can be minimized by
utilizing proper location and design features. Applications for marinas shall
include a comprehensive site plan showing location and number of all
water-dependent and upland facilities such as parking and storage
facilities.
(c) New marinas, which
includes all structures defined as marinas in
30-1(D),
are not allowed in waters classified for shellfish harvesting, except for any
locked harbor, dry stack or expanded existing marina that does not close any
additional waters for shellfish harvesting.
(i) An applicant for any marina in waters
classified for shellfish harvesting, can request that the S.C. Department of
Natural Resources (DNR) comment in writing on whether the area around the
proposed marina is suitable or not suitable for the natural growth and
propagation of shellfish. The permit shall not be issued unless the Department,
after giving great weight to the comments of the DNR, determines that natural
physical conditions in the area surrounding the proposed marina preclude the
natural propagation of shellfish.
(ii) The DNR's comments shall be based on
criteria including:
(1) intertidal bottom
types (including shell matrix depth and composition - shell, clay,
silt);
(2) density of naturally
occurring oyster beds (oyster strata types, bottom coverage,
acreage);
(3) presence or absence
of significant subtidal oyster populations;
(4) water depth;
(5) oyster population elevations;
(6) salinity regimes (including a review of
historic data and recognition of possible future changes that could affect
hydrography);
(7) presence or
absence of significant clam populations;
(8) potential for expansion of existing
natural oyster beds through cultivation;
(9) potential for shellfish production with
non-traditional methods;
(10) the
current shellfish management and water quality classifications;
(11) and any other factors relating to the
natural physical conditions in the area deemed appropriate by the DNR including
whether the area is likely to support the natural growth and propagation of
shellfish in the reasonably foreseeable future.
(iii) This determination in no way affects or
limits the ability of DNR to comment on the entire permit application before
the Department.
(d)
Marinas should be located in areas that will have minimal adverse impact on
wetlands, water quality, wildlife and marine resources, or other critical
habitats;.
(e) Marinas must extend
to the first navigable creek, within extensions of upland property lines or
corridor lines, that has a defined channel as evidenced by a significant change
in grade with the surrounding marsh; or having an established history of
navigational access or use. Rare geographic circumstances, such as very close
proximity of a significantly larger creek within extensions of property or
corridor lines, may warrant marina extension to a creek other than the first
navigable creek. A creek with an established history of navigational use may
also be considered as navigable. Such creeks cannot be bridged in order to
obtain access to deeper water. However, pierheads must be located over open
water and floating docks which rest upon the bottom at mean low tide will not
normally be permitted. In exceptional cases, the Department may allow an open
water channel to be bridged if other man made or natural restrictions prohibit
current access or if site-specific conditions warrant such a
crossing.
(f) To be eligible for a
marina, a lot must have a minimum of 150 feet of frontage at the marsh edge,
and 150 feet between its extended property lines at the location in the
waterbody of the proposed structure.
(g) No marinas or other associated structures
will be permitted closer than 20 feet from extended property lines with the
exception of common marinas shared by two adjoining property owners. However,
the Department may allow construction closer than 20 feet or over extended
property lines where there is no material harm to the policies of the
Act.
(h) Existing permitted and
grandfathered marinas as of the effective date of these regulations may be
maintained and rebuilt to their pre-existing size and configuration if damaged
or destroyed. However, these marinas cannot expand beyond their current
footprint if such expansion violates the requirements of 30-12.E(1)(f) and (g).
Marinas that do not meet the frontage and offset requirements of 30-12.E(1)(f)
and (g) may expand channelward provided all other applicable Department
standards are met. Additionally, at such time as these marinas expand, even
when remaining within their existing footprint, a permit will be required and
applicable Department standards, including 30-12.E(2) and (3) relating to
operation and maintenance, must be met.
(i) Marinas proposed for the exclusive use of
occupants of the adjoining development will only be permitted in lieu of
multiple private docks. Eliminating private docks on small creeks in exchange
for permitting a marina with private slips on a larger waterbody is the
preferred alternative of the Department. To determine the number of slips
allowed within this type of marina, a ratio of 2.5 to 1 or 50 feet of slip
length for every private dock (or lot served by a joint use dock) eliminated
will be utilized. No leasing, or other transfer of space to individuals who do
not reside in the community or other commercial uses are allowed at these
marinas.
(j) Marinas shall not
restrict the reasonable navigation or public use of State lands and
waters.
(k) Marinas shall be
constructed in a manner that does not restrict water flow and must avoid or
minimize the disruption of currents. Dead-end or deep canals without adequate
circulation or tidal flushing will not be permitted.
(l) The size and extension of the marina must
be limited to that which is reasonable for the intended use.
(m) Marinas should use the least
environmentally damaging alignment.
(n) Where marina construction would affect
shellfish areas, the Department must consider the rights of the lessee, if
applicable, and the public, and any possible detrimental impacts on shellfish
resources.
(o) Marinas should be
located in areas where the least initial and maintenance dredging will be
required. New marinas that require initial and maintenance dredging must
provide a permanent, dedicated spoil area capable of holding both the initial
dredge volume and all anticipated maintenance needs. This spoil area must be
reserved using deed restrictions or other legal instruments.
(p) Marinas must avoid or minimize the
disruption of currents. Dead-end or deep canals without adequate circulation or
tidal flushing will not be permitted.
(q) Marina design must minimize the need for
the excavation and filling of shoreline areas;.
(r) Open dockage extending to deep water is
preferable to excavation for boat basins, and it must be considered as an
alternative to dredging and bulkheading for marinas;.
(s) Turning basins and navigation channels
shall be designed to prevent long-term degradation of water quality. In areas
where there is poor water circulation, the depth of boat basins and access
canals should not exceed that of the receiving body of water to protect water
quality.
(t) Project proposals
shall include facilities for the proper handling of petroleum products, sewage,
litter, waste, and other refuse in accordance with Department
regulations.
(u) Dry storage type
marinas are preferred whenever feasible, and an applicant for a marina permit
will be required to show why a dry storage facility is infeasible, in whole or
in part. Infeasibility may be shown where the applicant seeks a facility for
large boats that cannot be accommodated in a dry storage facility or where
there is inadequate upland space for the facility.
(v) Applications for marinas must include
maintenance dredging schedules and dredged material disposal sites when
applicable.
(w) Adequate parking
for users of the marina shall be demonstrated as either one parking space for
every three wet and/or dry slips or the spaces required by the applicable local
government parking regulation, whichever is greater.
(x) Mooring fields associated with marinas
are encouraged in place of pierheads and floating docks where the size of the
waterbody and other site specific conditions are suitable. These mooring fields
must be in compliance with R.30-12(P).
(2) The following standard conditions, along
with any special conditions that may be appropriate, will be included in all
permits for marinas unless the Department determines that such standard
conditions are inappropriate
(a) The
operations of the marina shall be reviewed by the Department as deemed
appropriate, but at least every five years. Based on this review, the
Department may require, among other things, changes or additions to the
Operations and Maintenance Manual to address any water quality or other
environmental problems, and a reduction in the size of, or a change in the
configuration of, the marina. Such action may be taken at any time the
Department determines that significant state water quality compliance problems
exist, at the time the Department enlarges the closure area, or at the time of
a review.
(b) A water quality
sampling program must be instituted and results submitted to the Department.
This sampling program must be performed prior to construction and as specified
in 30-12(E)(3)(c)below. This sampling must be performed by a Department
certified laboratory at the expense of the permittee. If water quality
monitoring indicates a decline in water quality, remedial action will be
required.
(c) Dredging must be
performed in accordance with 30-12(E)(3)(d) and 30-12(G).
(d) A stormwater plan for the marina and
associated parking areas, including runoff from the permanent spoil disposal
area and adjacent highland development, must be submitted to and approved in
writing by the Department staff before any work is performed under the
Department permit.
(3)
The Operations and Maintenance Manual shall be submitted with the application
and placed on public notice. This requirement may be waived at the discretion
of the Department upon a determination that the uses of the facility warrant
such a waiver. Depending on the type of facility, it shall contain the
following information:
(a) Marina Operations
(i) An experienced operator shall be in
charge of the marina. The permittee and its agents are responsible for
compliance with the issued Operations and Maintenance Manual and with all
conditions of the permit.
(ii) The
marina permittee must include in the lease agreement with boat owners a
provision requiring that boat owners comply with all applicable State and
federal regulations. The marina permittee shall ensure that violations are
reported promptly to the proper authorities.
(iii) A complete copy of the marina permit,
including any required marina report, the Operations and Maintenance Manual,
all conditions or requirements placed on the permit and copies of all water
quality monitoring reports required pursuant to the permit, shall be readily
available at the marina.
(iv) The
marina permittee shall prominently display and distribute material pertaining
to the maintenance of water quality standards at the marina and report
violations of such standards to the proper authorities.
(b) Water Quality Management:
(i) Adequate working wastewater pump-out
facilities shall be provided at each marina (unless specific exceptions are
allowed in writing by the Department). These facilities must be adequate to
handle all wastewater generated at the marina. The marina operator may charge a
reasonable fee for the use of the pump-out facilities.
(ii) Adequate bathroom facilities must be
provided in order to discourage any overboard discharge of sewage from boats.
The number of toilets required for any given marina shall be determined by the
nature and size of the marina and by its specific site location. However, two
toilets and one lavatory for women and one toilet, one urinal, and one lavatory
for men shall be required for all marinas with one hundred or fewer slips, and
unless there are mitigating circumstances, the Department shall require one
toilet and one lavatory for women and one toilet, one urinal, and one lavatory
for men for every additional 100 boat slips or fraction thereof. Toilet
facilities shall be constructed in a location to encourage their use.
Additional facilities may be required where restaurants, motels, laundries, and
other nonwater-dependent structures are located in close proximity to the
marina. All pump-out and sewage facilities must be included in the public
notice and certified in writing by the Department.
(iii) Plans for potable water supplied to the
marina docks must be approved in writing by the Department.
(iv) Marina boat fueling systems must be
equipped with emergency cutoffs at the harbor master's office, at the tank, at
the pump and at the dock's edge.
(v) Depending on the size and type of boats
using the marina, adequate booms must be available to isolate any oil spill
around the fuel dock, a leaking boat, or a sunken boat.
(vi) Absorbent pads must be available at the
marina for boat use and for removing incidental spills during fueling
operations.
(vii) The discharge of
sewage from boats is prohibited unless it is treated by a Marine Sanitation
Device and complies with all applicable federal laws and regulations. The
discharge of any other kind of waste into state waters, including, without
limitation, garbage, refuse, trash or debris, is prohibited.
(viii) Adequate separate refuse containers
for garbage shall be available at the marina and maintained daily. Containers
for toxic substances shall not be placed over or near the water.
(ix) Boat repairs, paint scraping, boat
painting, and other activities that may result in a discharge of waste or
pollutants into State waters are prohibited;
(x) One reasonably sized dock master's office
may be constructed within a permitted marina. This office will be limited to
water dependent uses only such as fuel sales. Restroom facilities may be placed
in this office, however, food and beverage services, clothing sales and other
non-water dependent uses are prohibited.
(c) Water Quality Monitoring Requirements The
specific program shall be determined by the Department. Any changes in
requirements must be approved in writing by the Department. Sampling results
must be supplied to the Department. The program may be discontinued or waived
by the Department upon a showing that such information is not necessary to
insure adequate protection of coastal resources.
(i) Monitoring requirements shall be tailored
to the marina based on factors such as flushing, existing water quality,
presence of shellfish, number of slips, and presence of fueling
facilities.
(ii) A minimum standard
monitoring program will consist of an annual sediment analysis. These samples
shall be taken once a year between June and August with a minimum of one
composite sample taken within the confines of the marina and one sample taken
outside the marina. All sampling sites must be approved in writing by the
Department staff and the DNR. Samples will be analyzed for polyaromatic
hydrocarbons, copper, zinc, lead, cadmium, chromium, and any other parameters
required by the Department
(iii)
Marinas in poorly flushed areas may be required to sample other parameters such
as dissolved oxygen and/or fecal coliform bacteria. These monitoring
requirements will be determined on a site-specific basis using the factors
presented in (i) above.
(iv)
Sampling requirements will be periodically reviewed and may be increased or
reduced as conditions warrant.
(d) Dredging:
(i) Unless otherwise allowed by permit, all
initial and maintenance dredging shall take place between December 1 and March
1, and all dredging shall be performed by hydraulic dredge.
(ii) Agitation dredging is
prohibited.
F. Transportation:
(1) There is often a strong public need for
transportation projects. Unfortunately, such projects can pose a significant
risk of environmental degradation. However, careful consideration of
environmental factors can guide development toward more favorable results. To
the maximum extent possible, environmental considerations shall be harmonious
with public safety considerations.
(2) The specific standards are as follows:
(a) In the planning of major transportation
routes and airports, these projects should be sited for location inland from
the critical areas;
(b) The
location and design of public and private transportation projects must avoid
the critical areas to the maximum extent feasible. Where coastal waters and
tidelands cannot be avoided, bridging rather than filling of these areas will
be required to the maximum extent feasible;
(c) Where wetlands will be destroyed, their
value as wetlands will be assessed by the Department and weighed against public
need for their destruction;
(d) To
the maximum extent feasible, transportation structures must be designed so as
not to alter the natural water flow and circulation regimes or create excessive
shoaling or erosion. Where applicable, adequate clearance for commercial and
pleasure craft must be provided;
(e) Where feasible, maximum care shall be
taken to prevent the direct drainage of runoff water from transportation routes
and associated facilities from entering adjacent water bodies;
(f) Where appropriate, bridges and approaches
should be designed to provide for the enhancement of public access by the
utilization of fishermen, catwalks, boat launching ramps, bike lanes and other
structural features;
(g) During the
planning of a multi-lane widening or improvement project, it is preferable to
follow the existing alignment in wetland areas. Existing causeway and fill
areas must be utilized wherever possible. The degree to which any existing
causeway through wetlands can be widened must be reasonably proportionate to
the expected traffic load of the causeway in the near future and the size and
use of the area being provided access. The width of medians of divided highways
must be reduced as much as possible wherever they cross wetland
areas;
(h) Roadway embankments and
fill areas shall be stabilized by utilizing appropriate erosion devices and/or
techniques in order to minimize erosion and water quality degradation problems.
Culverts shall be required, where appropriate, in order to maintain normal
tidal influence and minimize disruption of drainage patterns;
(i) The Department will require applicants
for transportation project permits to consider the accommodation of other
public utilities in facility design, thus avoiding unnecessary future
alteration such as that caused by the laying of cables or transmission lines in
wetlands adjacent to an existing roadway;
(j) New road or bridge projects involving the
expenditure of public funds to provide access to previously undeveloped barrier
islands will not be approved unless an overriding public interest can be
demonstrated.
G. Dredging and Filling:
(1) Development of wetland areas often has
been considered synonymous with dredging and filling activities. Dredging and
filling in wetlands can always be expected to have adverse environmental
consequences; therefore, the Department discourages dredging and filling. There
are cases, however, where such unavoidable environmental effects are justified
if legitimate public needs are to be met.
(2) The specific standards are as follows:
(a) The creation of commercial and
residential lots strictly for private gain is not a legitimate justification
for the filling of wetlands. Permit applications for the filling of wetlands
and submerged lands for these purposes shall be denied, except for erosion
control, see R.30-12(C), or boat ramps, see R.30-12(B). All other dredge and
fill activities not in the public interest will be discouraged;
(b) Dredging and filling in wetland areas
should be undertaken only if that activity is water-dependent and there are no
feasible alternatives;
(c) To the
maximum extent feasible, dredging and filling activities should be restricted
in nursery areas and shellfish grounds and during periods of migration,
spawning, and early development of important sport and commercial
species;
(d) Dredging and
excavation shall not create stagnant water conditions, lethal fish entrapments,
or deposit sumps or otherwise contribute to water quality
degradation;
(e) Designs for
dredging and excavation projects shall, where feasible, include protective
measures such as silt curtains, diapers, and weirs to protect water quality in
adjacent areas during construction by preventing the dispersal of silt
materials;
(f) Dredged materials
shall be deposited and contained in such a manner so as to prevent dispersal
into adjacent wetland areas and, in all cases, new facilities must have
permanent upland disposal sites. Existing facilities must have either permanent
upland disposal sites or EPA approved ocean disposal sites;
(g) Applications for dredging in submerged
and wetland areas for purposes other than access, navigation, mining, or
drainage shall be denied, unless an overriding public interest can be
demonstrated. Dredging permits for mining will be issued only as specified in
(2)(h) below. Drainage permits must be consistent with the provisions in
R.30-12(L);
(h) Applications for
dredging for mining activities within the critical areas will be denied unless
a significant portion of the resource is located in the critical area,
extraction of the resource is clearly necessary, and benefits derived from
extraction would outweigh resultant detrimental impacts on coastal ecosystems.
For any permit issued to allow dredging for mining operations in the critical
areas, a complete site reclamation plan shall be required;
(i) Wetlands shall not be utilized as
depositories for waste materials except as discussed in R.30-12(I and
J);
(j) In all cases, dredging
activities shall not be approved until satisfactory disposal sites have been
acquired.
(k) Only hydraulic
dredging is permitted unless the material is being placed in a hopper barge for
offshore disposal or unless the applicant can show that hydraulic dredging is
infeasible in a site-specific application.
(l) Marinas will usually not be allowed in
areas that require maintenance dredging more often than once every four
years.
H.
Navigation Channels and Access Canals:
(1)
Certain dredging activities involve the creation and maintenance of navigation
channels and access canals. These activities have a potential for severe
environmental impacts and should meet a demonstrated public need.
(2) Where the Department determines that such
activities are justified, the following standards will be applied:
(a) Dredging for establishment of new canals
which involves permanent alteration of wetland habitats will be prohibited
unless no feasible alternative exists. Establishment of canals for purposes of
creating waterfront lots from inland property will be prohibited unless it can
be demonstrated that there will be no significant environmental impacts on
critical areas;
(b) To the extent
feasible, project plans must utilize piers or catwalks, rather than channels or
canals, to reach deeper water areas;
(c) Access canals shall be designed to insure
adequate flushing and shall not create dead-end or stagnant water pockets.
Open-ended, U-shaped, or semicircular canals are generally preferred over
dead-end canals, since they usually provide better water circulation;
(d) Highland waterway construction that is
slated to be tied into wetland areas shall be constructed in the dry, if
feasible, so that sloping and stabilization of the banks can be completed
before the plug is removed for the connection to open waters. Where dry
construction is not possible, temporary plugs or silt curtains at the end of
canals connected to waterways should be maintained until all sediment settles
out;
(e) The sides of navigation
channels and access canals should be gently sloping rather than vertical to
facilitate biological as well as physical stabilization of the canal
banks;
(f) When several landowners
are to be served by a project, dredging for navigation channels and access
canals should be well planned to prevent unnecessary excavation. Tributary
canals in the highlands leading to a central navigation channel should be
utilized rather than separate channels for each waterfront landowner;
(g) The berm of access canals should be
raised so that there is a gradual slope away from the canal edge. This will
help prevent introduction of contaminants into adjacent wetland
areas;
(h) Alignment of channels
and canals should make maximum use of natural or existing channels. Alignment
of channels and canals should avoid shellfish beds, nursery areas, and spawning
areas in wetlands.
I. Deposition of Dredged Material:
(1) The deposition of dredged materials
resulting from numerous dredging activities along the coast has serious
environmental effects separate from the original dredging activity. Thousands
of acres of productive wetland habitat have been destroyed by such deposition.
Recognizing that additional disposal sites will be required, it is important
that site acquisition proposals include plans for mitigating any adverse
impacts upon the environment.
(2)
The following standards are to be utilized:
(a) Upland disposal of dredged material shall
always be sought in preference to disposal in wetlands. Vegetated wetlands and
mudflats shall not be utilized for disposal of dredged materials unless there
are no feasible alternatives. Any other wetlands should not be utilized for
disposal of dredged materials when other alternatives exist;
(b) Open water and deep water disposal should
be considered as an alternative if highland alternatives are not feasible.
However, open and deep water disposal sites should be seriously considered only
after careful consultation with the Department and other relevant State and
Federal agencies;
(c) Dredged
materials containing hazardous levels of toxic material must be disposed of
with extraordinary caution. These materials shall never be disposed of in
wetland areas and only in highland areas which are lined and diked with
impervious materials. These materials will only be disposed in open water ocean
dumping sites when maximum safety has been demonstrated after thorough review
by the Department and other appropriate state and federal agencies;
(d) Dikes surrounding disposal areas should
be shaped and vegetated immediately to minimize erosion, with outfalls
positioned to empty into non-wetland areas;
(e) Future disposal sites shall be reviewed
on a case-by-case basis;
(f)
Wherever feasible, existing disposal areas shall be utilized to the fullest
extent possible; this would include raising the height of the embankments to
increase the holding capacity of the disposal area;
(g) Consideration must be given to the
temporal aspects of spoil deposition - for example, impacts on spawning, fish
migrations, shellfish harvesting, waterfowl nesting and wintering areas, and
mosquito control. Attention must be given to possible adverse impacts of
various alternative sites on the public health and welfare as well as on
critical fish and wildlife areas;
(h) In all cases, dredging activities shall
not be approved until satisfactory disposal sites have been acquired.
J. Waste Treatment
Systems:
(1) The Department regulates the
installation and operation of waste water treatment facilities, septic tanks,
and landfills. Normal maintenance and repair of sewer facilities are exempted
from the Department permit requirements by Section
48-39-130(D).
The discharge of treated effluent is also exempted; provided, however, that the
Department shall review and comment on these discharges. The Department is
concerned primarily with wetland degradation problems which could involve
commercially important shellfish, recreational fisheries, and critical wildlife
habitats.
(2) Standards applicable
to these installations are as follows:
(a)
Applications for the construction of lagoons or impoundments for waste
treatment facilities, solid waste disposal sites and similar activities in the
critical areas shall be denied unless there are no feasible alternatives and it
can be demonstrated that there will be no significant environmental
impacts;
(b) Wherever feasible,
construction and design of waste treatment facilities shall be accomplished in
such a manner that no effluent will be discharged into areas where shellfish
and other marine resources would be adversely affected. Where waste treatment
facilities would affect open, productive shellfish harvesting areas, the
Department must consider the rights of the lessee, if applicable, or the public
in the case of public oyster grounds, as well as impacts on shellfish
resources;
(c) The siting of sewage
treatment systems should avoid the critical areas. The location of structures
other than actual pipelines, such as pump or lift stations, in critical areas
will be prohibited unless no feasible alternatives exist;
(d) The construction of sewage treatment
facilities and associated discharge pipes should be located and designed so as
not to have adverse impacts upon areas of significant public use.
K. Marsh Impoundments
for Recreational and Commercial Activities:
(1) Marsh impoundments totaling nearly 69,000
acres comprise a significant portion (approximately 16 percent) of our coastal
wetlands. An additional acreage, perhaps equaling this figure, has been
impounded in the past but consists today of tidally influenced areas where
embankments are no longer maintained. Once important rice growing areas, the
majority of these impoundments are managed primarily for recreational waterfowl
hunting, wildlife sanctuaries, and other commercial, agricultural, and
preservation uses.
(2) Proposals
will be reviewed on a case-by-case basis according to the following standards:
(a) Permit applications to impound previously
unimpounded wetlands or areas inundated by Outstanding Resource Waters shall be
denied unless an overriding public interest is clearly demonstrated.
(b) The following factors will be considered
in the review of permit applications for the impoundment of wetlands:
(i) Condition of existing dikes. Projects
should require a minimum of new bank construction in wetlands.
(ii) Amount of wetlands proposed to be
impounded.
(iii) The extent to
which the project would block waters presently used for recreation or
navigation by the public.
(iv)
Degree of salinity of waters impacted by the proposed project.
(v) Quality of waters affected by the
proposed project.
(vi) Primary
purpose of the impoundment.
(c) All applications for the impoundment of
wetlands must be accompanied by a detailed management plan setting forth the
intent and method of managing the impounded areas. The management plan must be
approved by the Department prior to permit issuance and shall become a
condition of the permit. This plan must contain, but not necessarily be limited
to, the following information:
(i) Applicant's
objective(s) for the impoundment.
(ii) Schedule of water level
manipulations.
(iii) Methods of
pest and predator control (i.e., use of pesticides, prescribed burning,
etc.).
(iv) Water quality
management plan.
L. Drainage Canals or Ditches:
(1) Drainage canals or ditches should follow
the least damaging alignment and should meet one or more of the following
needs:
(a) insect or vector control as a
public health necessity;
(b) other
public health purposes;
(c) the
control of runoff as part of a comprehensive flood plain management plan.
Upland treatment of runoff is required if new drainage ways are permitted in
critical areas.
(2) In
addition to the application standards for dredging and filling and navigation
channels and access canals, the following standards shall apply:
(a) Drainage canals and ditches shall not
create dead water or stagnant pockets;
(b) To the extent feasible, the alignment of
drainage canals should avoid the more productive wetlands;
(c) To the extent feasible, alignments of
canals shall make maximum use of existing deep water channels to avoid
unnecessary excavation;
(d) To the
extent feasible, the quantity and quality of any discharged waters shall not
result in extensive alteration of wetlands or the quality of coastal
waters;
(e) All dredged material
must be disposed of in accordance with the regulations under
R.30-12(I).
M. Nonwater-Dependent Structures:
(1) Nonwater-dependent structures, as defined
in Section R.30-1(D), have been built in the past on pilings, moored or in
other ways situated over coastal water and/or tideland critical areas. These
structures are a serious threat to the values set forth in Section
48-39-20(E).
(2) Nonwater-dependent structures, including
buildings, houses, or offices that float shall be prohibited from being
constructed, moored, or otherwise placed in or over tidelands and coastal water
critical areas unless there is no significant environmental impact, an
overriding public need can be demonstrated, and no feasible alternatives
exist.
(3) The Department shall at
its discretion determine on a case-by-case basis whether or not a floating
structure is a boat and thus exempt from the Act or in fact is a
nonwater-dependent structure. This shall be based upon the primary function of
the floating structure. The mere fact that a structure is registered as a
vessel or capable of being propelled does not mean it is exempt from the
Department regulations.
N. Access to Coastal Islands. This section
applies to applications for permits for bridges and docks as a means of
obtaining access to coastal islands.
(1)
Purpose and Intent:
(a) South Carolina has
several thousand coastal islands, including barrier islands, sea islands, back
barrier islands and marsh hammocks. Almost all of these islands are surrounded
by expanses of salt marsh, occasionally bordered by tidal creeks or rivers.
Historically, few of these islands have been built upon or altered, and most
have been protected by their remoteness and inaccessibility. In recent years,
however, a trend toward greater potential for development of these islands has
stimulated questions and concerns about the ecological significance of these
islands. The South Carolina Department of Natural Resources conducted a field
study of a number of non-barrier islands. Their report, An Ecological
Characterization of Coastal Hammock Islands, December, 2004, has shown that
these islands are unique ecosystems with diverse flora and fauna. That study
recommends protection and buffering of important habitats and resources
associated with these islands.
(b)
Access to coastal islands by bridges or docks involves the placement of
structures into critical area coastal tidelands and waters that are protected
by the statute, the critical area regulations, and by the public trust
doctrine.
(c) Construction of
bridges within critical area tidelands and waters involves impacts on critical
area coastal tidelands and coastal waters, including temporary damages to salt
marsh and shellfish beds, temporary increased turbidity, permanent displacement
of marshes by installation of pilings, and permanent shading of
marsh.
(d) The requirements of
R.30-12.N apply only to islands for which a bridge or dock permit is issued,
and are not intended to apply to upland areas or to otherwise modify, alter,
conflict, create precedent or otherwise impact existing regulations and
law.
(2) Eligibility to
apply for a bridge permit.
(a) The decision on
whether to issue or deny a permit for a bridge to a coastal island must be made
with due consideration of the impacts to the public trust lands, critical area,
coastal tidelands and coastal waters, weighed against the reasonable
expectations of the owner of the coastal island. Giving due consideration to
these factors, the Department has determined that some islands are too small or
too far from upland to warrant the impacts on public resources of bridges to
these islands, and thus no permit for a bridge shall be issued.
(b) Bridge permits, other than non-vehicular
bridges for access by the general public, will not be issued in areas of
special resource value unless they qualify under the special exceptions in
R.30-12.N(10). These are the ACE Basin Taskforce Boundary Area, the North Inlet
National Estuarine Research Reserve, and the Cape Romain National Wildlife
Refuge.
(c) The Department will not
consider applications for bridge access to islands less than two acres in
size.
(d) The Department will,
however, consider applications for bridge access in the following instances:
(i) Bridges not exceeding 15 feet in total
width
(a) where the size of the island is two
acres or greater, but less than or equal to three acres, and the distance from
the upland and the length of the bridge does not exceed 200 feet;
(b) where the size of the island is greater
than three acres but less than or equal to five acres and the distance from the
upland and the length of the bridge does not exceed 300 feet;
(c) where the size of the island is greater
than five acres, but less than or equal to ten acres and the distance from the
upland and the length of the bridge does not exceed 500 feet.
(ii) Bridges may be constructed
exceeding 15 feet in total width
(a) where the
size of the island is greater than 10 acres, but less than or equal to 30
acres, and the distance from the upland and the length of the bridge does not
exceed 500 feet;
(b) where the size
of the island is greater than 30 acres and the distance from the upland and the
length of the bridge does not exceed 1,500 feet.
(e) Notwithstanding the provision
of R.30-12.N(2)(c), the Department shall consider applications for bridge
access to coastal islands greater than one acre in size if the distance from
the upland is 100 feet or less in distance.
(f) All measurements to coastal islands for
the purpose of establishing whether an island may qualify for a bridge permit
are taken from upland as defined in this section.
(i) Upland is:
(a) the naturally occurring mainland,
and
(b) Waites Island in Horry
County; Pawleys Island in Georgetown County; Isle of Palms, Sullivans Island,
Folly Island, Kiawah Island, Seabrook Island, Edisto Island, Johns Island,
James Island, Woodville Island, Slann Island and Wadmalaw Island in Charleston
County; Daniel Island in Berkeley County; Edisto Beach in Colleton County;
Harbor Island, Hunting Island, Fripp Island, Hilton Head Island, St. Helena
Island, Port Royal Island, Ladies Island, Spring Island and Parris Island in
Beaufort County.
(ii)
The length measurements for all proposed bridges will be taken from a current
Department approved critical area line. The length of a bridge is defined as
the distance between critical area lines at each end of the bridge.
(g) In order to apply for a bridge
permit, the applicant must submit a survey, produced and stamped by a
registered surveyor licensed to practice in South Carolina, showing that the
length of the proposed bridge will not exceed the lengths allowed in these
regulations.
(3) Dock
and Bridge Construction Standards Associated with Coastal Islands.
(a) Docks.
(i) The following standards apply to docks in
projects associated with applications for bridge access to coastal islands. The
project standards in this section are in addition to the other Department
standards applicable to docks.
(ii)
The application for the project shall reflect that the applicant has eliminated
75 percent of the number of private residential docks allowed by the
Department's critical area permitting regulations as they existed on September
1, 2005. The dock reduction shall be made binding on the land by a conservation
easement meeting the requirements of R.30-12.N(4).
(iii) Docks longer than 500 feet over the
critical area are prohibited. This is inclusive of pierheads, floats, ramps,
mooring piles and other associated structures.
(iv) No boat lifts, davits or similar
structures are allowed.
(v) Roofs
are not allowed on private docks, but are allowed on community docks.
(vi) All docks proposed for an island must be
shown on a dock master plan that is submitted with the bridge
application.
(b)
Development Plan.
(i) All bridges shall be the
minimum possible size and height to accommodate the intended use, aligned to
minimize environmental damage, and constructed of materials approved for marine
applications.
(ii) The applicant
must submit a site development plan.
(c) Lighting on bridges must be designed with
the minimum illumination necessary to meet local, state, or federal
requirements for safety and navigation.
(d) All utilities servicing the island must
be located within the footprint of the bridge and attached to the bridge if
feasible, but must not be placed overhead.
(e) Onsite Disposal Systems (OSDS). If the
island is to be served by OSDS, all alternative systems must meet a horizontal
setback requirement of 150 feet from any part of the OSDS to the Department
critical line.
(4)
Conservation easements. Whenever a reduction in environmental impact is either
required or offered, the affirmative commitment must be accomplished by a
conservation easement, the conservation easement must meet the requirements of
this part.
(a) The conservation easements
shall be prepared in accordance with the South Carolina Conservation Easements
Act of 1991, S.C. Code Ann. Section
27-8-10
through
27-8-120,
and any amendments thereto (the "Act").
(b) The conservation easements must provide
for permanent protection in perpetuity that will run with the title to the
land.
(c) The conservation easement
must incorporate by reference a recorded plat that depicts the environmental
impact reduction. Once the conservation easement and associated plat are
properly recorded in the chain of title, the failure to show the required
delineations on a future plat shall not affect the validity of the conservation
easement.
(d) The conservation
easement must be held by the state or a land trust with a proven track record
in the region and with the resources to enforce the terms of the easement. The
conservation easement must provide for rights of enforcement by the Department
and by any organization authorized to be a "holder" under the Act, provided
that any legal action by a party other than the Department taken to enforce the
terms of the conservation easement must include the Department as a party, and
no such action may be settled without the written consent of the
Department.
(e) Draft conservation
easements must be submitted to the Department for review to determine
compliance with the Act and the applicable limits and commitments related to
the permit at issue, prior to issuance of the bridge permit.
(f) Prior to commencement of any work under a
permit issued under this section, the recorded conservation easement must be
filed with the Department, accompanied by an opinion of an attorney duly
licensed to practice in South Carolina, certifying that the instrument has been
duly executed by the fee simple owners of the property, that the individual
signers of the instrument have full legal authority to execute the instrument,
that the instrument has been properly recorded and indexed in the office of the
county Register of Deeds, and that all holders of prior mortgages or other
liens on the property have consented to the instrument and have subordinated
their liens to the conservation easement.
(5) The owners of bridges are entitled to
repair and maintain existing bridges as allowed under R.30-5.D and any
applicable county or municipal regulations.
(6) If an existing bridge to a coastal island
is destroyed or rendered unusable by natural causes or accidental destruction,
the owner shall be entitled to a permit to replace the bridge with a like
bridge that imposes no greater adverse impact on the critical area as the one
destroyed.
(7) Permits for
expansion of existing bridges will be processed as new bridges and must meet
all applicable standards.
(8)
Causeways.
(a) Permanent filling of critical
areas for access to coastal islands is prohibited, except for fill associated
with existing useable causeways.
(b) Existing useable causeways are defined as
those causeways that have a drivable lane above the critical area.
(i) Permits for fill associated with existing
usable causeways shall be granted only for minor fills that are minimized by
use of containment structures to limit to the maximum extent feasible the
square footage of fill, and where the fill would cause less damage to the
critical area than would be caused by construction of a new bridge or other
access structure.
(ii) Mitigation
for critical area fill at a ratio of 2:1 will be required for fill associated
with existing usable causeways.
(9) Non-vehicular bridges to be utilized by
the general public on publicly owned lands for purely recreational,
educational, or other institutional purposes will be exempt from all other
sections of R.30-12.N and will be allowed by the Department provided there is
no significant harm to coastal resources and the following minimum standards
are met.
(a) The applicant must demonstrate
that the structure is necessary for the overall planned use of the
site.
(b) The structure must be
aligned to minimize environmental impacts.
(10) Special Exceptions.
(a) Islands one acre or larger that do not
qualify for a bridge permit under these regulations may apply for a special
exception. To receive a special exception, the applicant shall present clear
and convincing evidence that granting the bridge permit will serve an
overriding public interest.
(b) For
an application to meet the overriding public interest test, it must demonstrate
by clear and convincing evidence that it will create overriding public benefits
resulting from mitigation and diminished impacts to public trust resources
compared with development that would likely occur without the bridge.
(c) All public benefits considered under this
exception must be secured by a permanent conservation easement meeting the
requirements of R.30-12.N(4) on all affected property.
(d) Impact reductions that the Department may
consider are:
(i) permanent protection of
habitat,
(ii) major reductions in
building density,
(iii) major
reductions in subdivision rights,
(iv) major reductions in docks,
(v) major increases in riparian
buffers,
(vi) other architectural
and site design improvements, and
(vii) minimization of bridge impacts to
environmental and visual resources.
(11) Severability Clause. In the event that
any portion of these regulations is construed by a court of competent
jurisdiction to be invalid, or otherwise unenforceable, such determination
shall in no manner affect the remaining portions of these regulations, and they
shall remain in effect, as if such invalid portions were not originally a part
of these regulations.
O.
Mariculture:
(1) Mariculture means the
confined cultivation of aquatic species in the marine environment, including
the spawning and rearing of juveniles and adults, either alone or in
combination with other species, and the trafficking in said species.
(2) Mariculture activity is increasing in the
coastal waters of the State and it can be expected to grow considerably in the
coming years. Overall mariculture activities have the potential to increase
food supplies and provide employment and with proper management can be a
compatible activity for the coastal critical areas. As with all activities in
these sensitive areas, there need to be controls to insure that disruptions
caused by such operations are minimized or eliminated and public trust issues
are properly addressed.
(3)
Specific standards which shall apply are as follows:
(a) No commercial mariculture operation will
be allowed within 50' of an existing dock or block access to such dock unless
conducted by the dock owner or with the dock owner's permission. If a dock is
later permitted and constructed in a mariculture area, any affected mariculture
operation must be moved to comply with this regulation.
(b) Each mariculture activity must file an
operations plan as an addendum to its permit application. This plan must be
complete and in the approved format before the application will be placed on
public notice. Written confirmation of this by the Department is required. The
applicant is advised this list is not all inclusive and other sections of
SCDHEC, as well as other agencies, may have additional requirements. The plan
must address:
(i) Description of proposed
activities, including intended use of products, with maps showing actual
coverage of critical area.
(ii)
Potential environmental impacts and their mitigation.
(iii) Potential conflicts with existing
co-users and their mitigation.
(iv)
Navigational issues and plans for marking areas and identifying confinement
structures.
(v) Steps taken to
guarantee removal of mariculture structures in case of abandonment.
(vi) Storm damage plan.
(c) All structures, such as holding pens,
shall be designed to be as unobtrusive visually as possible, with navigational
markers meeting Coast Guard requirements, if any.
(d) All mariculture permits will be
conditioned to require the permittee to agree to adopt Best Management
Practices (BMP's). These BMP's must be updated as industry standards and
technology changes.
(e) Private,
non-commercial mariculture operations will be limited to no more than two
hundred square feet of growing surface. These operations will be permitted only
if the permittee owns the adjacent highland and is a riparian property
owner.
(4) If a proposed
mariculture activity complies with the standards stated in this regulation, a
permit shall be issued unless the Department concludes that the activity is
inconsistent with the basic state policies contained in Section
48-39-30,
or that the activity is contrary to the public interest in that the proposed
activity would unreasonably conflict with existing public uses; the proposed
activity would unreasonably interfere with navigation; or the proposed activity
would be otherwise inconsistent with the Coastal Zone Management
Program.
P. Mooring
Buoys:
(1) Mooring buoys provide moorage for
vessels in open water areas. Mooring buoys, however, may cause navigational
problems and hazards.
(2) Specific
standards which shall apply to the placement of mooring buoys are as follows;
(a) Mooring buoys may be used to moor private
or commercial vessels. Mooring buoys for private waterfront property owners
shall be limited to one buoy per property, must be placed within extended
property lines and placed on the same side of the channel as the property. No
more than two vessels may be moored to the buoy at any time;
(b) With the exception of pumpout facilities,
no commercial activity including, but not limited to, food services, T-shirt
sales, concessions and boat maintenance services, may be allowed on or around
moored vessels;
(c) There shall be
no discharge of waste from vessels moored to buoys. Examples of such waste
includes, but is not limited to, sewage, garbage and debris;
(d) Permits for private mooring buoys will
only be issued to adjoining highground property owners. The mooring diameter
(extent of vessel swing) does not allow the moored vessel to swing within 20
feet of extended property lines;
(e) The mooring buoy's anchor(s) must be of a
type and or weight to prevent drag of the buoy and must be clearly indicated in
the permit application;
(f) The
mooring buoy shall be a minimum of 18 inches in diameter, be made of pliable
material and have sufficient reflective material so it may be seen at night.
The buoy shall have the owners name, address and permit number placed on the
buoy with at least one inch letters and must be legible at all times;
(g) If the mooring buoy becomes an impedance
or hazard to navigation, it must be removed or relocated by the permittee upon
request by the Department. Failure to remove a mooring buoy shall result in
permit revocation.
(3)
The cumulative impact of private, single family mooring buoys may lead to
navigational impedance and these concentrations may be considered a marina type
facility. Therefore, developers and communities are encouraged to create and
utilize limited mooring fields for the restricted use of the community property
owners. These limited mooring fields should be in conjunction with a community
docking structure and/or boat ramp for access.
Q. Living Shorelines: Living shorelines, as
defined in 30-1.D, are encouraged as an alternative to traditional hardened
erosion control structures in estuarine environments because they provide an
environmental benefit and reduce the environmental impacts associated with
hardened structures. Living shoreline methods involve planting of native
vegetation and/or the installation of other green infrastructure. Green
infrastructure includes softer approaches to protecting estuarine shorelines
and consists of materials that promote growth of native biological components
and maintain continuity of the natural land-water interface. Environmental
conditions of a site will be considered in the evaluation of living shoreline
applications including whether the type of living shoreline has demonstrated
success. Demonstrated success can include an increase in the presence of native
vegetation and/or oysters, and an increase in elevation on the landward side of
the living shoreline installation.
The following standards are applicable for all living shoreline installations:
(1) Living shorelines
are limited to waterfront parcels or lots as defined in R.30-1.D.
(2) Living shorelines must be constructed
within extended property boundaries of the permittee for individual projects.
One application may be submitted for a living shoreline installation that
involves more than one adjoining waterfront parcel. The Department may consider
an alternative alignment on a site-by-site basis if site-specific
characteristics warrant such an alignment.
(3) Living shorelines must be shore parallel
and aligned to conform to the natural contours of the shoreline to the maximum
extent feasible.
(4) Living
shorelines must not be installed in creeks less than twenty (20) feet in width
as measured from marsh vegetation on each side unless special geographic
circumstances exist. In all cases, the Department will consider any
navigational concerns when evaluating the siting of living shoreline
projects.
(5) All living shoreline
applications must demonstrate that the installations are designed to promote
growth of native biological components. Only native vegetation may be used if
the site is planted. Living shoreline installations must be composed of
Department approved materials. Approval of materials by the Department may
require the applicant to submit a certified letter from the supplier of the
source material.
(6) The size and
extent of the living shoreline must be limited to that which is reasonable for
the intended purpose. All living shoreline applications must demonstrate that
the living shoreline is designed and constructed in a manner that:
(a) does not restrict the reasonable
navigation or public use of state lands and waters;
(b) has minimal effect on natural water
movement and in no case prohibits water flow;
(c) does not prevent movement of aquatic
organisms between the waterbody and the shore;
(d) maintains, restores, and/or enhances
shoreline ecological processes;
(e)
maintains continuity of the natural land-water interface; and
(f) prevents the installation from being
displaced which can result in marine debris.
(7) Filling or excavation of vegetated
tidelands for the construction of a living shoreline is prohibited. Minimal
impacts to non-vegetated tidelands may be permitted to achieve a successful
installation only if no feasible alternative exists. Projects with proposed
non-vegetated tideland impacts must provide sufficient evidence that no
feasible alternative exists and must demonstrate avoidance and minimization of
impacts. Construction of living shorelines must not disturb established, live
shellfish beds. Living shoreline installations must not be constructed in a
manner that results in the creation of upland.
(8) Living shorelines must be maintained by
the permittee such that the installation is generally intact and functional.
The Department may require the permittee to monitor the living shoreline
subject to the critical area permit to determine whether the installation is
functioning as intended, results in marine debris, or impedes navigation or
public use of state lands and waters.
(9) The Department may require remediation or
removal of a living shoreline for reasons that include, but are not limited to:
(a) the installation is no longer generally
intact and functional;
(b) the
installation has resulted in marine debris;
(c) the installation impedes navigation or
public use of state lands and waters; or
(d) the installation is not accomplishing the
intended purpose of the living shoreline.
(10) If a living shoreline is destroyed by
natural events, the installation may be rebuilt to its previously permitted
configuration so long as reconstruction is completed within one (1) year of the
date of the event unless there are extenuating circumstances justifying more
time.
Notes
State regulations are updated quarterly; we currently have two versions available. Below is a comparison between our most recent version and the prior quarterly release. More comparison features will be added as we have more versions to compare.
No prior version found.