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COMMENTS ON HILTON HEAD ISLAND E. I. S. BY NANCY CATHCART GROUP OF THE S. C.
SIERRA CLUB CHAPTER
!§
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The Nancy Cathcart Group of the S. C. Sierra Club Chapter strongly
opposes the strategy that the discharge of treated effluent should be allowed
into the surface waters (Calibogue Sound) off Hilton Head. Our position is
that NO discharge of treated effluent to the surface waters around Hilton Head
Island should be permitted.
Treated water is a resource and should be used on Hilton Head Island,
not dumped off island. Land application — using natjural infiltration techniques
in wetlands, golf course and sports fields -- should be employed where feasible.
The surface waters around Hilton Head Island are generally pristine
estuarine environments. We must not set the precedent that inland waters (such
as Calibogue Sound) make useful dumps for sewage or any other material.
Secondarily treated sewage contains nutrients that could overload
sediments with nitrogen and phosphorous. If there are low currents at sub-
surface levels of inland waters, this overloading could impact the aerobic-
anaerobic balance of decomposition of bottom matter.
We urge E. P. A. to investigate these effects and how well inland
waters can flush pollutants using long term research based on firm biological
and hydrological data. Our estuaries are critical habitats too vital to all
living things here to be impacted by a short-sighted, easy-way-out solution
to an effluent problem which may very well have ipnovative, useful solutions.
The solution for disposing treated effluent should include the entire
island, not just one public service district. Wastewater should be recycled
island-wide. Public service districts should develop tertiary treatment plants
which further purify wastewater and remove nitrogen and phosphorous. Drinking
water can be produced by tertiary treatment. This would provide a guaranteed
drinking water supply and would conserve pur "dwindling ground water reserves.
Certainly, recycling drinking water from tertiary treatment would be a wiser
investment than pumping water from the Savannah River, which could be further
impacted by future industrial pollution.
Wastewater can be returned to our aquatic marshes and swamps. Here
effluent is filtered by plantlife and absorbed by the spongy soil of the water-
shed. This process is called "Natural Infiltration". Other areas which could
benefit from limited irrigation of wastewater are golf courses, lawns, sports
fields, power easements and highway median plantings.
The Sierra Club urges E. P. A- to reject dumping effluent into the
surface waters of Hilton Head Island and to focus on more creative solutions
to waste disposal problems which would involve sound biologic principles
and conservation techniques.
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Mr. E. T. Heinen
July 7, 1982
Page 2
3, A long-term program of frequent shallow watertable
monitoring in areas relying upon septic tank systems
H should be undertaken by the Beaufort County Health
Department and Department of Health and Environmental
Control.
4. In areas served by central collection and treatment
csj systems, no new septic tank systems should be allowed or
^ old systems replaced.
^ 5. The long-term goal should be removal pf all septic tank
§ systems from the Island as central treatment systems
£ become available.
H
—With kindest regards,
CG/jl
C&drih--
/¦* - j. _ l_ w'
Charles Gatch
Executive Director
'r>r
iJr? a
.» 4 v
fr
M JUL 13 198*
3ISV
KPA-!;v'j
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Charl'-o P. Gohon, Jr.
P .ft. Rox
Myrtle Island
Blufr'ton, C.C. 29910
July 7, 1382
United States Environmental Protection Agency
3^5 Court land
Atlanta, Ga. 303&5
Re: Hilton Head E15 Statement
Gentlemen:
I hope you took note of the fact that at the public
hearing of the EIS, not the first developer 'from Hilton
Head addressed the meeting. I feel that the developers have
the EPA locked up in their hip pocket and did not wish to
attend the meeting and rock the boat.
It is more than obvious that you people have lost sight
of the word ENVIRONMENT in your name and should make immediate
arrangements to change it to the Developers Protective Associa-
tion of H i1 ton Head.
The marshlands are the bread basket of the food chain of
marine life. Your proposal of dumping into the sound can only
have a detrimental effect. You certainly cannot show a plus.
The South Carolina Coastal understands this much better than
On the subject of federal aid to assist dumping into the
sound, do you know that Sea Pines, as well as the other plantations,
are PRIVATE. There is a guard at every enterance and the public is
turned away. If the sewerage outfall into the sound comes to past,
it could make an interesting court case.
I have never had much cortfidence in any government bureau-
cracy and your EIS certainly bears this' out. This time you put
the money down the sewer instead of the usual rat hole.
It has been about 120 years since the last Yankee invasion
and at that time Sherman laid waste from the mountains to the sea.
V/e now have a Yankee invasion of Hilton Head and the developers
with your aid will lay waste to the ecology of this area.
you people.
CCOjL'i'*.
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HILTON HEAD NO. 1 PUBLIC SERVICE DISTRICT
Industrial Park Road — Post Office Box 1264
Hilton Head Island, South Carolina 29925
Telephone 803 - 785-5525
July 6, 1982
To: E. T. Heinen, Environmental Assessment Branch
From: Hilton Head Number One Public Service District
Re: Draft EIS for Hilton Head Island, South Carolina
1. The Commissioners of the Hilton Head Number One Public Service
District ( District ) offer the following comments on the Draft
EIS for Hilton Head Island, as it relates to future planning and
development within the District:,
A. General
The draft EIS does not adequately "...address the provision
of wastewater management facilities to serve existing and future
needs", as stated in the purpose of the EIS on page 1-1 , para-
graph 1.
B. Population Projection
There is a large disparity between the OBERS population projec-
tion and the actual population. This; disparity impinges on the
demand for wastewater flows. In the District's case, actual flows
have already exceeded the OBERS projected flows for the year
20 00. In addition, the criteria used for the OBERS, as well as
the JPC population projection should have been presented in a
separate appendix in order that their differences may be eval-
uated, and that any assumptions uged in the projection could be
compared to the growth actually occuring on the Island, In this
way, the original projection could be updated to a more accurate
figure.
CM
OS
i§
S
to
N
"No Action" Alternative
The decision to present the "no action' alternative for areas
whose present population and/or wastewater flows have already
exceeded the OBERS projection is not consistant with the stated
purpose of the EIS. While these "no action" areas are no longer
eligible for federal funding, this should not preclude a dis-
cussion of the available alternatives¦for wastewater management
in order that a comprehensive assessment may be established for
the Island and be available to all Districts for their future
planning needs. As the EIS is now written, it is primarily
applicable to the Sea Pines Public Service District and is not
of value to the Island as a whole. It should be noted that in
Title 40? part 1500, (Preparation of Environmental Impact State-
ments: Guidelines, established by the Council on Environmental
Quality), Section 1500.5 (Types of actions covered by the Act),
paragraph 2 states tha't " '.actions' include but are not limited
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Draft EIS for Hilton Head Island
Page Two
to: new and continuing projects and program activities...
supported in whole or in part through federal contracts, grants,
The District is presently being funded by the EPA for
construction of new wastewater facilities; therefore, while
the District is no longer elibible, it is using federal funds
and should not be included in the "no action" alternative.
2. In conclusion, the District feels that the Draft Environmental
Impact Statement for Hilton Head Island does not adequately
describe the existing environmental conditions, nor does it ful-
fill it's stated purpose. Therefore, the District recommends that
the responsible agency re-evaluate the criteria used to develop
the EIS; re-evaluate their assesment of existing conditions;
and re-evaluate their recommendation based upon it's effect on
the future planning and development of Hilton Head Island as a
total community.
Respectfully submitted,
Melville B. Coburn
Chairman
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REPLY TO
ATTENTION OF:
DEPARTMENT OF THE ARMY
SAVANNAH DISTRICT. CORPS OF ENGINEERS
P. O. BOX 689
SAVANNAH. GEORGIA 31402
SASPD-EI
7 JUL 1982
Mr. E. T. Heinen
Chief, Environmental Assessment Branch
Environmental Protection Agency, Region IV
345 Courtland Street, N.E.
Atlanta, Georgia 30365
Dear Mr. Heinen:
Reference is made to your Notice of Public Hearing dated 30 April 1982
and the Draft EIS on Hilton Head, South Carolina Wastewater Facilities,
which was forwarded to my office by the U. S. Army Corps of Engineers,
Washington, D. C.
My comments are attached as Inclosure 1. I would appreciate the opportunity
to comment on any further actions concerning the project.
1 Incl
As stated
Copy Furnished:
USACE (DAEN-CWP-V) WASH DC 20314
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COMMENTS ON HILTON HEAD WASTEWATER DEIS
Issue No. 7
Cultural Resources. Locating the sites through survey would not be adequate
mitigation. The EPA needs to indicate that they will comply with current
legislation and regulations to avoid or mitigate impacts to significant
cultural resources.
Regulatory Functions. Construction of the alternative treatment facilities
and discharge structures will likely require Department of the Army authoriza
tions. Hilton Head Island lies within the regulatory jurisdiction of the
Charleston District; review for regulatory purposes requires coordination
with SACOP-P. However, the scope and detail of a DEIS for a 201 facilities
plan is not amenable to determination of regulatory requirements.
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RECEIVED JUL 1 5 1982
South Carolina Coastal Council
James M. Waddell, Jr.
Chairman
H. Wayne Beam, Ph.D
Executive Director
June 17, 1982
Mr. Charles Jeter
Environmental Protection Agency
345 Courtland Street, N.E.
Atlanta, Georgia 30365
Re: Environmental Impact Statement for
Hilton Head Island, S.C. Wastewater
Facilities
Dear Charlie:
The South Carolina Coastal Council has completed its review of the
Draft Environmental Impact Statement for Hilton Head Island, S.C. Wastewater
Facilities. Pursuant to the policies of the South Carolina Coastal Zone
Management Plan and 15 CFR Part 930: Consistency for Department of the
Interior Outer Continental Shelf Prelease Sale Activities and for Other
Federal Activities Directly Affecting the Coastal Zone, an alternative
method allowing the discharge of secondarily treated effluent into
Calibogue Sound is not consistent with the policies of the South Carolina
Coastal Council. The Hilton Head Island Special Area Management Plan
(Chapter Two, Section I, Item C) states that "no discharge of primary or
secondarily treated effluent into the critical areas of Hilton Head Island"
shall be allowed.
Whereas we do recognize that the EIS, as issued on April 30, 1982,
is still in draft form, please be advised of the Coastal Council's concern
and intentions. Should the final EIS contain this alternative in a design
which would not satisfy our consistency requirements, the Coastal Council
would be obliged to submit a negative determination at the appropriate time.
We realize the difficulties associated with providing the necessary
infrastructure to support development, however, the Coastal Council's
responsibilities as mandated by the South Carolina General Assembly, remain
directed toward the preservation and enhancement of a sound natural
environment for future generations. We appreciate your deliberations, and
look forward to working with you to bring about an acceptable solution.
Sincerely,
H. Wayne Beam
Executive Director
HWB:jnk
cc: Senator James M. Waddell, Jr.
Mr. Duncan C. Newkirk
«?rat| Center, 19 Hagocd Street. Suite 802 » Cv-ii«v ~ W* tfe-xant
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DEPARTMENT OF THE ARMY
Charleston district, corps of engineers
P O BOX 9 1 9
CHARLESTON SC 2&402
AT7CNTIOS Of
SACEN-E
14 May 1982
fir. E. T. Heinen, Chief
Environmental Assessment Branch
EPA, Region IV
345 Courtland Street, N.E.
Atlanta, Georgia 30365
Dear Mr. Heinen:
Issue No. 7
We have reviewed the draft EIS for waste-water facilities at Hilton Head,
South Carolina and have no comments in connection with environmental
considerations. However, it appears that a Department of the Army permit
will be required for some of the proposed alternatives.
Should you have any questions concerning Department of the Army "permits,
please telephone Mr. A. B. Gould at (803) 724-4610.
Sincerely,
Copy furnished:
Office, Chief of Engineers
ATTN: DAEN-CWP-V
WASH DC 20314
'ARMJPrrr CROUSE
Chief, Engineering Division
Division Engineer, South Atlantic
ATTN: SADPD-R
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DEPARTMENT OF THE AIR FORCE
REGIONAL CIVIL, ENGINEER, EASTERN REGION (HO AFESC)
»2C TITLE BUILDING, »0 PRVOR STREET. S.W.
ATLANTA. GEORGIA 30J03
ATTN or, R0V2
12 May 1982
tuajECT: Draft Environmental Impact Statement (DEIS), Hilton Head, South Carolina
Wastewater Facilities
to. U. S. Environmental Protection Agency
Region IV
Attn: Mr. E. T. Heinen
Chief, Environmental Assessment Branch
3I+5 Courtland Street, N. E.
Atlanta, Georgia 30365
1. As the Air Force central point of contact for intergovernmental
coordination of environmental planning matters in Federal Regions I - IV,
we have reviewed the subject DEIS and find that development of the proposed
project will have no impact on Air Force operations in South Carolina.
2. Thank you for the opportunity to review this DEIS. Our point of contact
is Mr. Winfred G. Dodson, FTS: 2^2-6821/6776.
Captain, USAF, Deputy Chief
Environmental Planning Division
bcolosiwl imm
^:A-P3T.''IV
1I I4KU* GA-
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MONTAGUF I UCKKK l.AI l-l'ITK
MYH'fl-f: ISLAND
I'OST OFFICE BOX 161
BI.UFFTON. SOUTH CAROLINA 29910
July 6, 1982
Me. E. T. Heinan
Chief, Environmental Assessment Branch
US Environmental Protection Agency# Region IV
345 Courtland Street
Atlanta, Georgia 30365
Dear Mr. Heinan: re: Hilton Head Island
Environmental Impact
I urge you to reconsider your Draft and recommend that no
discharge of treated effluent be allowed in Calibogue Sound.
Yours truly,
Montague T. Laffitte
MTL/kcb
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L. P Strudle Jn.
3 KILLDCCR LANE
HILTON HEAD ISLAND. 8. C.
28828
July 1902
L. T. Heinan
Chief - iiiviorninental 'Assessment Branch
U. S. imviorrunental Protection Afrency
Region IV
345 Courtland Street
Atlanta, Georgia 30365
Dear Sir:
T wish to enter this statement in regard to the EIS
discussed at the Hilton Head island Elementary School
on J„ne 23, 1982.
I moved to Hilton Head Island in 1978 and one of the
chief reasons for coming here was to fully en.ioy and
exploit the marine life in the waters around the Island.
In the winter I gather oysters for my own consumption at
the Public Oyster Grounds. During the rest of the year
I fish off-shore, in-shore and in the bays and sounds.
Already these activities have been threatened by pollution.
s
I further ob.iect to discharge in our waters because there can
be no careful control on the quality of the effluent. Kech-
canical breakdown, human carelessness or outright violation
of the laws can go along unnoticed until the area waters
have been seriously polluted.
If any further permits are made for proper sewage treatment,
1 think:'they should be reserved for effluent from ^ewexs
that will replace the septic tanks on the Island. If any
capacity remains, after consideration of normal home growth,
the balance of capacity may be assigned to.multiple housing
or commercial units.
Thank you.
Very truly yours,
Partially treated effluent makes the consumption of shell
fish unhealthy and dangerous. If the effluent is treated
to the extent that it does not cause pollution of shell
fish, it will have so much chlorine and other chemicals
in it that all marine life will be endangered. Food and
breeding grounds for sea life will be ruined and eventually
we will have little or no marine life in our waters.
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May River Committee
Preserve Our Estuary
Box 391, Bluffton, S.C. 29910 757-3470 and 757-3248 „
June 28, 1982
E.T.Heinen, Chief Re: Hilton Head Island
EPA Region IV Environmental Impact
Atlanta, Ga Statement
Dear Mr. Heinen:
Our committee cannot support EPA's recommendation
as to discharging effluent into Calibogue Sound. You have not
provided data to support your conclusion.
Attached is our fact sheet in more detail than the
one we sent you in February. This new fact sheet elaborates on
but does not supercede our previous letter.
Our Committee will be ready by Fall to work with you
on the complex challenge of dealing with the '208' program.
Carroll 0. Dailey
for May River Committee
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May River Committee
Preserve Our Estuary
Box 391, Bluffton, S.C. 29910 757-3470 and 757-3248
DATA SHEET - RE. EFFLUENT DISCHARGE INTO CALIBOGUE SOUND
The May River is merely an arm of the Sound (embayment). As
such no fresh water flushes it and thus it becomes a trap for
accumulating flotsam, DUtrients, viral, pathogens, chlorine
and whatever might be introduced to its waters. Attention
has not been by EPA in its E.I.S. draft to this potential
for pollution.
Issue No. 6
DYE STUDY
We are aware Sea Pines Public Service District has made a
study through a professional engineering firm to determine
dispersion data on effluent discharge. Since we have not
seen the report, our information is incomplete, being based
on newspaper reports. We have misgivings about this study
for reasons stated below.
Dye tests were made on Mar. -18, 1982, when,
according to NOAA current charts, the current was least for
the entire year.
It is generally accepted that discharge must be
intermittant to coordinate with the ebb tide current. The
tests were made on a 1.1 knot flood tide. (Port Royal Sound
Study of 1972 released dye on the ebb tide in the Colleton
River in an amount of 750 lbs with approximately one fifth
the volume.pf Braddock Point where 50 lbs were used.)
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May River Committee
Preserve Our Estuary
Box 391, Bluffton. S.C. 29910 757-3470 and 757-3248
CURRENT INFORMATION
Maximum Currents during 1982 at Braddock Point
32°' 07.1'N 80501 W
Spring Flood 3.2 knots Spring Ebb 3.3 knots
Neap " 1.1 " Neap " 1.9
Average Flood 2.2 " Aver. " 2.5 "
Currents for Three Dates in 1982
June 23 Flood 2.7 knots Ebb 3.3 knots
Mar 18 " 1.1 " " 1.8 "
April 8 " 2.4 " " 2.7
Generalized Information on Current Patterns
A spring flood tide entering Calibogue from the south
meets the flood tide coming down from Port Royal at the May
River mouth. The western side of this current from the south
continues without interruption into the May River. On the
easterly side of the Sound there is great turmoil where the
two flood tides meet at May River entrance. With its much
larger volume the tide from south rides over the small current
and continues to Port Royal Sound where it turns immediately
along the north shore of thg Island eastward and then southerly
along the coast.
Other Miscellaneous Data
References have been made about releasing the effluent
in deep water as a means of dispersion. There is no water
deep enough in Calibogue for such dispersion (50'-60') since
the effluent immediately rises to the surface when released
into saltwater.
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ASPPPO
Association of Sea Pines Plantation Property Owners, Inc.
Post Office Box 5704
Hilton Head Island, S.C. 2993S
Telephone 785-7721
TFKMS EXPIRE
Tt l'i ujry
DjvuI M, BiKlu'ltirf
ElL>* rt G. Bellows
W. [\jLhard Cafhcarl
Ben {. Grant
Mark L. Sluppy
June 28, 1982
BOARD OF DIRECTORS
February I9S-5
Paul Freeman. Jr.
Willard ). Harm>;. Vice President
Helen C. Scott
Edward J. Kuscl. President
John |. Min^ay
ADMINISTRATOR
Woodlord Montgomery
February
Richard T. Clark
Walter L. lor\4ru\ mv
James H. Simpson. Se>.ty. Trea-
Alfred \V Wolff
John H. Wyss
Mr. E. T. Heinan
Chief, Environmental Assessment Branch
U.S. Environmental Protection Agency, Region IV
345 Courtland St.
Atlanta, GA 30365
Subject: Environmental Impact Statement
covering Hilton Head Island
Good morning, Mr. Heinan:
Issue No. 3
The Board of Directors of the Association of Sea Pines Plantation
Property Owners Association, Inc. urges the granting of an extension
to the Sea Pines Public Service District for discharge of excess treat-
ed effluent into the Lawton Canal. This extension should be for a
reasonable period of time not to exceed five (5) years. Furthermore,
the effluent must be given tertiary treatment and the Sea Pines PSD
must seek out additional on island land areas for spray irrigation in-
cluding privately owned landscaped areas, road medians, etc.
This extension will give the various agencies involved the necessary
time to determine the most cost effective method of disposing of this
excess discharge in the future. As of this date, these agencies are
not in agreement indicating there are still many questions to be an-
swered. Certainly they must await the completion of the 208 study
since storm water run off is the major pollutant to be dealt with in
a total plan for Hilton Head Island.
If the tertiary treated effluent can be used for other purposes
such as spray irrigation of privately owned landscaped areas and road
medians which now use our drinking water, we will conserve significant
founts of potable water for use by future generations.
Thank you for your consideration.
Cordially
Suite ]0, Elguin Building — 41 Bow Circle — Palmetto Bay Center
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South Can illiid
Hi It/life kH Marine
Resources Department
James A. Timmerman, Jr.. Pn 0
Executive Director
Pat Ryan
Director of
Law Enforcement and Boating
J. Stephen Hopkins
Marine Resources Division
SCWMRD
P.O. Box 478
Port Royal", S.C. 29935
24 June 1982
Mr. E.T. Heinan
Chief, Environmental Assessment Branch
US Environmental Protection Agency, Region IV
345 Courtland St.
Atlanta, GA 30365
Dear Mr. Heinan,
Issue No. S
The Marine Resources Division of the S.C. Wildlife and Marine
Resources Dept. would like to issue a few comments concerning the
Draft Environmental Impact Statement for Hilton Head Island Waste-
water Facilities, Our position, with regards to the'disposal of
wastewater, has not changed since the inception of this study in
May 1979. However, the preferred alternative outlined in the draft
does not meet with our approval so we find it necessary to reiterate
our objection to the disposal of wastewater in the marine environ-
ment. This objection is based upon the adverse impacts of a number
of pollutants which one would expect to find associated with the
Sea Pines - Forest Beach PSD effluent as well as the deleterious
precedent it would set for other coastal developments. These poll-
utants include, but are not limited to, excessive levels of nutrients,
disinfecting agents, viruses, heavy metals, pesticides, BOD and fresh
water.
As mentioned in previous letters to EPA concerning this same
situation, it is feared that the nutrient load in the effluent from
the Sea Pines waste treatment facility, as well as future outfalls
from new developments, could have adverse impacts on the marine food
chain. It has been established that the species composition of the
phytoplankton community is sensitive to changes in the level of various
nutrients as well as the ratio of nitrogen:phosphate. For instance,
nutrient overloading and low N:P ratios tend to favor such species as
Nanochloris sp. and Stichoccus sp. These algae are consumed by the
American Oyster but are an inferior nutrient source. Thus, oyster
production is decreased. A decrease in oyster production will impact
upon the recreational and commercial oyster fisheries as well as the
physical characteristics of the estuary. Oyster reefs play an essen-
tial role in the formation of tide pools which are highly utilized by
a variety of organisms. In addition, oysters influence the water tur-
bidity by depositing suspended particulate matter (100 lbs. of sediment
P. O. Box 167 ~ Dutch Plaza ~ Building D ~ Columbia, South Carolina 29202 ~ Telephone: 803-758-6736
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per year per square yard of reef).
Dense blooms of algae, resulting from nutrient overloading, will
also affect the biological oxygen demand. In some instances, the BOD
is intense enough to result in an oxygen depletion, killing a variety
of marine organisms and lowering total production.
The changes in the ecosystem mentioned above, while serious in
themselves, are overshadowed by a yet more damaging agent. Research
conducted.over the past few years has shown that the addition of large
quantities of chlorine to the marine environment is extremely damaging.
The best example is the Chesapeake Bay where-/the cumulative effect of
a large number of treated sewage outfalls is believed by some to be
the primary agent responsible for the declining fishery resources in
what has historically been the largest seafood producing area in the
country. The problem in that area is perceived to be so serious that
the Tidewater Administration of the state of Maryland may back a bill
in that legislature to ban all chlorinated discharges to surface waters.
The toxic affects of chlorine has been demonstrated for a large number
of marine organisms, many of which exist in Calibogue Sound and it's
tributaries. A few examples of.organisms to which chlorine is toxic
are the Rockfish or striped bass (Morone saxatilis), Spotted Seatrout
(Cynoscion nebulosus), Spot (Leiostomus xanthurus), Atlantic Siversides
(Menidia mendia), Blue Crabs (Callinectes sapidus), Mud Crabs (Panopeus
herbstii), Hermit Crabs (Pagurus longicarpus), Hard Clams (Mercenaria
mercenaria), American Oysters (Crassostrea virginica), and lower down
the food chain, a copepod (Acartia tonsa).
Several fish kills in Maryland have been attributed to chlorine
toxicity. In addition, a 1977 report to the U.S. Congress by the Comp-
troller General encouraged EPA to stop unnecessary and harmful levels
of domestic sewage chlorination. The idea of chlorinating a marine
outfall to prevent bacterial contamination of shellfish is self-defeat-
ing. As the volume of the discharge increases in response to continued
development you approach a situation where the shellfish are safe to
eat, if you can find any that are still alive. In addition, disinfect-
ing agents are not completely effective in destroying certain viruses
which may become concentrated in filter feeders.
Another adverse impact of wastewater discharges is the toxic
affects of trace metals and their geochemical deriviatives. Trace
metal contamination is often thought of as being associated with
industrial discharges. However, it has been found that trace metals
are present in fairly high concentrations in municipal wastewater
discharges as well. When freshwater polluted with "dissolved" trace
metals enter the marine system, the metals and their derivatives
are rapidly deposited in the sediment through floculation and pre-
cipitation of colloids. The toxicity of these compounds varies from
species to species. Some organisms are killed outright through ab-
sorption or ingestion. Other benthic animals and algae accumulate
the pollutants and pass them on to organisms higher up the food chain.
In this way, the trace metals may be distributed throughout the estuarine
system and later passed on to man at locations far removed from the
actual discharge pipe.
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Inevitably, pesticides also make their way into municipal waste-
water discharges. The adverse effects of pesticides upon marine life
is well documented and its pathways are often similar to that of cer-
tain trace metals as discussed above.
Even the fresh water which is released via a marine discharge can
have an adverse effect on the systems total productivity. The salinity
gradients around Hilton Head are already being impacted by the increase
in runoff as a result of land use changes. An additional five million
gallons per day just stresses the system that much more. As salinities
change, stenohaline species are displaced and the species diversity
dwindles. It is just one more way in which man disrupts an ecosystem
which has evolved to make the best use of the' natural conditions. Even
if the toxic effects of many components of the discharge are overlooked,
the abrupt (in an evolutionary sense) changes resulting from water qual-
ity manipulation will result in long term productivity reductions while
the system is shifting towards a new equilibrium.
We agree with statements in the draft EIS which note that non-
point source pollution is of a greater magnitude than the point source
discharge. However, we do not agree with assertions made 'by the PSD
representatives that the Lawton Canal 'discharge is of "better" quality
than the surrounding creek water. It is "better" only in the sense
that it contains fewer col-iform bacteria as a result of heavy chlorina-
tion. Of course, the bacteria are in no way harmful to the marine life
while the discharge has a variety of components which are either toxic
or disruptive to the food chain as discussed above. While non-point
source pollutants do contain compounds which are hazardous to both
humans and marine life, their presence should not preclude efforts to
abate further degradation of the water quality through a point source
discharge.
While the Marine Resources Division is concerned only with the
protection of the marine environment, some comments relative to EPA's
apparent commitment to "cost-effective" solutions seem in order. First,
the cost projections presented in the draft EIS are too simplistic in
nature. Data has been presented on the present net worth and projected
annual user costs for the various disposal alternatives. However, no
attempt has been made to evaluate the effect of these various alterna-
tives on such things as property values, the tourist trade, commer-
cial fisheries, etcs.., Since the island's clean environment is of
paramount importance in determining the success of fisheries, tourism
and real estate investments, hedging on the costs of wastewater dis-
posal at the expense of the surrounding environment would be false
economy. In addition, your "cost-effective" solutions would result in
minor savings on the Sea Pines - Forest Beach PSD sewer bills at the
expense of all the citizens of Beaufort and Jasper Counties who util-
ize the marine resources of the area for recreation or a livelihood.
In a yet larger sense, marine resource user groups along the entire
South Carolina Coast would be forced to endure a hardship, in the form
of environmental degradation, as a result of the precedent set on
Hilton Head for marine wastewater disposal from new development.
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-'1-
We strongly urge EPA to recommend that marine disposal of waste-
water be prohibited and that the present outfall in Lawton Creek be
eliminated, by whatever means, immediately. With the elimination of
the buffer zone around Lawton Creek we can begin to work on methods
of controling the non-point source pollution and, hopefully, return
all the waters around the island to the pristine state in which Sea
Pines found them, twenty-five years ago.
J. Stephen Hopkins
Regional Marine Biologist
Office of Conservation, Management
& Marketing
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[jI.I'AC I Ml.N T Ol III. AL III HUMAN SI KVIC.l.S
Centors for Disease Cc".
Atlanta, Georgia 30333
(404) 262-6649
June 25, 1982
Mr. John E. Hagan, III, P.E.
Acting Chief, Environmental.Assessment Branch
Environmental Protection Agency, Region IV
345 Courtland Street, N.E.
Atlanta, Georgia 30365
Dear Mr. Hagan:
We have completed our review of the Draft Environmental Impact Statement (EIS)
for Hilton Head, South Carolina, Wastewater facilities. We are responding on
behalf of the U.S. Public Health Service.
Since water quality data have indicated that non-point source pollution from
stormwater run-off is a severe problem and may worsen, we agree that EPA
funding should be dependent upon the development of a non-point source control
program within the public service district (PSD). We note, however that
at present there is no existing authority or legislation for implementing
such a program (page IV-4). We suggest that the final statement elaborate
on steps being taken by the PSD to ensure that an appropriate agency receives
the authority necessary to implement the recommendations provided by EPA.
We have reviewed the subject EIS for potential vector-borne disease impacts
No serious vector problems are expected as a result of this project.
We appreciate the opportunity to review this draft document. Please send us
a copy of the final statement when it becomes available.
Sincerely yours,
Frank S. Lisella, Ph.D.
Chief, Environmental Affairs Group
Environmental Health Services Division
Center for Environmental Health
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6 Hummingbird Court
Hilton Head Island
South Carolina 29928
June 23, 1982
!§
8
E. T. Heinen, Chief
Environmental Assessment Branch
EPA, Region IV
3kS Cnurtland Street, N.E.
Atlanta, Georgia 30365
Dear Sir:
The Hilton Head Island members-at-large unit of the
of Women Voters has studied the final draft of the "Environmental
Impact Analysis Statement for Hilton Head Island Wastewater
Facilities", dated February 1982. It.is our value judgement
that none of the alternatives listed in this document is com-
pletely satisfactory as a solution to the problems associated
with wastewater management on the island. The League commends
those agencies involved in this document for their diligent and
comrehensive study thus far, but urges them to oontinue seeking
other, more satisfactory solutions.
The League fully agrees with DHEC that effluent must be
treated. Our recommendation is for tertiary treatment to do
lorm and reeling. ar® against the discharge of treated
.sewage into the waters around Hilton Head Island which mav k.
[harmful not only to island residents, but also to neighboring
communities. There must be assurance that any proposal to dis-
charge wastewater downstream does not result in the domino
leffect where the last property owner suffers.
No alteration of existing waterways, lagoons, ponds, rivers
streams, etc. should be allowed unless a change would inceease '
the filtering of non-point run-off and not adversely affect the
natural drainage systems or existing waterflow.
The League urges support for policies to reduce the non«
essential part of waste streams and the* recovery of the non-
reducable portion so as to ensure safe disposal of the rest.
This would preclude dumping in areas where shellfish harvesting
tthd recreational fishing would be severely affected and would
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E.T. Heinen, continued
result in loss of income to many native islanders.
The section on Mitigative Measures makes it clear that
there must be cooperation by Beaufort County. Such measures
as reduction of impervious surfaces of parking areas, etc.,
on-site retention or percolation of run-off, the use of wet-
lands for purification of storm water run-off, not overloading
wetlands which may harm natural vegetation, and encouraging
erosion and sedementation controls on sites adjacent to bodies
of water, are the areas in which local government must act in
order to lessen the impact of population growth on the envi-
ronment.
<2>
s
to
i?
The League study of the Environmental Impact Statement
raises a question which we ask respectfully. Has the EPA
ever considered the possibility and feasibility of consolidation
of all the Public Service Districts and the independent Waste
And Sewage Companies on Hilton Head Island as an alternative?
If not, then may we suggest such a study which may reveal that
the financial burden on any one segment of the island may be
lessened. Also, that golf courses which do not have available
treated effluent to meet their irrigation needs at this time
may benefit from the excess treated effluent of other areas
on the island. The mechanics of exercising condemnation au-
thority for land acquisition may be simplified. Duplication
of facilities and services may be eliminated and the problems
of Hilton Head Island wastewater disposal could be taken oare
of on the island where it originates.
At this point in time it appears that even the experts
cannot agree. Therefore, the League cannot presume to have a
final solution. We ask only that there be further study to
seek the alternative which would assure waters that are safe
to swim in, habitable for acquatic life, free of nuisance
conditions, and usable for commercial and recreational fishing.
This is imperative for the health, safety, and economy of this
island.
Yours truly,
'Wancy Ann Ciehanski, President
Hilton Island MAL Unit,
League of Women Voters
Above presented before a Public Hearing on June 23, 1982
at the Hilton Head Elementary School by
Beatrice P. Chait, Hilton Head Island Unit - Secretary
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COMMENTS AND RECOMMENDATIONS
for
U.S. ENVIRONMENTAL PROTECTION AGENCY'S
DRAFT ENVIRONMENTAL IMPACT STATEMENT
FOR HILTON HEAD ISLANDSOUTH CAROLINA
As presented for Public Hearing on June 23, 1982.
Submitted by
THE HILTON HEAD ISLAND COMMUNITY ASSOCIATION, INC.
June 23, 1982
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u!;conni:i;DATiot;s
Any plan for disposing of effluent generated on Hilton
Head Island should be approved by all governmental
agencies charged with protecting the area's environment.
Approval should be based on evidence from preliminary
on-site tests, and/or implementation of the plan at
other similar locations, demonstrating that the plan
will have negligible, adverse effects^ on the environ-
ment .
Such approval should be required for plans to correct
existing problems, or to increase the capacity of an
existing system, or to install a new system.
Any plan for disposing of.effluent should be cost-
effective for current users in the area to be served.
a. The plan should not risk creating a problem the
solution of which would require additional '
capital investment or increased operating costs.
b. The plan should not risk creating problems which
would affect other areas.
c. If the plan is to correct a problem resulting
from system design or installation, either no
cost should be imposed on current users, or the
plan should return to the area a benefit other
than the problem's correction.
An island-wide plan for sewage treatment and disposal
should be created and implemented. Such a plan would
help avoid problems arising from piecemeal, uncoor-
dinated development of sewage systems on the island
would facilitate the maintenance of standards and '
would aid the cause of orderly development. '
The plan should include:
a. Development of an extensive water quality baseline
for the entire island, as recommended by the EIS
b. Ascertainment of the capacities for effluent
absorption for all areas of the island This
information could help to determine advisable
rates and extents of developments.
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KirO.'iMEHUATlOHS (conI. )
Island-wide plan, (cont.)
c. Study, or restudy of disposal sites and methods
other than presented in the EIS. These might
include:
(1) Irrigation of roadsides, medians and/or
private property.
(2) Recycling of purified water through the
potable water supply via aquifers and/or
storage tanks.
(3) Anaerobic generators.
d. The development of better controls and/or more
stringent enforcement of existing regulations,
as recommended by the EIS. (111-20, IV-6)
e. Encouragement, to the extent possible, of water
conservation techniques by public and private
water users, as recommended by the EIS. (II-6)
Vigorous pursuit of regulation and correction of non
point source pollution. This would include the
continued development of techniques as well as
development of regulation and enforcement procedures
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COMMENTS
In addition to the people, the environment oi Hilton Head
Island is its most important asset. The climate, the land,
the waters and the air all undergird the island's economic
and social base.
The high quality of this environment attracts people and
their investments in homes, businesses and vacations. The
island will remain a potent attraction so long as it retains
a high environmental quality.
Our comments and recommendations are keyed to the EIS's
objective, which is "to select a wastewater management pro-
gram of Hilton Head Island that is compatible with the
protection of the area's sensitive resources, particularly
water quality, while recognizing the existing extensive
development pressures." (xiv, D)
The topics we address are, in order.
1. Protection of the area's resources.
2. Extensive development pressures.
3. A wastewater management program for HHI,
-3-
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rkovi.e'i'j o;j of the area • s hkhoui.cls
Planning and Monitor a ncj
The importance of planning is illustrated by Sea Pines'
current problems.
Plans for the disposal of effluent from the Sea Pines 2.0
MGD plan could not, in 1978, be entirely accomplished; the
golf courses could not accept the amount of effluent being
produced. To relieve the golf courses, about 3/4 of the
effluent was discharged into Lawton Canal. (III-J-12) Thus
the original plan, to use only the 'golf courses, was only
about 25% effective and, in addition contributed to contami-
nating the waters associated with the Lawton Canal. (II-7)
Continued population growth will call for continued expan-
sion of our sewage treatment systems. If planning for that
expansion is no more effective than the Sea Pines example
just cited, our region will be faced with a problem of truly
impressive magnitude as the island and the neighboring main-
land approach buildout.
Because planning involves so many complex variables, because
no comprehensive plan exists, and because unanticipated
problems have been experienced here, we suspect that any
plan will risk some degree of failure. To minimize that
risk, we recommend that all governmental agencies charged
with protecting the area's resources approve plans for
effluent dinposa] before implementation is permitted.
- 4-
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Monitor i ihj provides regulating cicjoncios w.i Lh information
on thn i;tate of our island, and indicates tho extent to
which plans work out in practice. Several monitoring
programs are already in effect or are being designed by
DHEC, S.C. Water Resources Commission, the Army Corps of
Engineers, and the Beaufort-Jasper Water'.Authority.
The EPA states that additional information is required for
the effective monitoring of our water quality. We endorse
the EPA's recommendation to develop a more extensive
water quality baseline of the entire island so that data
exist against which to measure future water quality changes
and assess significance of changes. (IV-7)
We also recommend that data gathered by DHEC, SCCC, EPA,
Rural Water Authority, S.C. Water Resources Commission,
the Army Corps of Engineers and similar agencies be
routinely shared with each other, and with the Beaufort
County Joint Planning Commission.
In addition to its other uses, the data should be used to
help determine island capacities, and thus rates and limits
for construction and land use in our region.
-5-
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LXTK.ns]vl; ;;EV»:i.oi»Mj:r:'r puF.sistiKK.j;
Much of Hilton Head Island's development complements the
high quality of nature's work. Our man-made environment,
including homes, accommodations for transients, and
sports facilities, help to make Hilton Head Island a
desirable place to visit and to live-
However, particularly because of information presented
in the Joint Planning Commission's State of the Island
Report, the community has become mpre acutely aware of
the extent to which development can degrade the quality
of living here, of the burdens that people put upon the
land and the waters. There is deep concern that.the
island's capacities will become irreversibly overburdened.
The "existing extensive development pressures" noted in
the EIS's statement of purpose must not be allowed to
force a decision in the selecting of a wastewater manage-
ment system. Those very pressures helped to generate
Sea Pines' present dilemma, and created a problem, the
solution of which will probably require residents of Sea
Pines and Forest Beach districts to pay increased costs
for no increase in services, (viii)
-6-
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The interests of Hilton Head Inland's residents and
visitors will be poorly served if the island's capacities
for safe disposal are exceeded, and if users must pay for
mistakes not of their own making.
To help protect the interests of the islana s residents,
visitors, and tourist industry:
1. We support the EPA's recommendations for the
development of better controls, and the more
stringent enforcement of existing regulations
as detailed in the EIS under "Mitigative Measures".
(111-20 et seq, IV-5 et seq)
2. We. recommend that any plan for correcting existing
problems or those which arise in the future, and
which will require additional financing or
operating costs, be cost-effective for current
users. That is, either no additional charge should
be made, or the additional cost should, beyond
correcting the problem(s), result in positive
benefits to the community.
-7-
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a wASvn-w.TKK pi,an koh miltoi! iikau isla:::j
The Hilton Head Island Community /association supported,
and continues to support South Carolina Coastal Council's
proposal that no discharge of effluent to the surface waters
around Hilton Head Island be permitted.
One concern about this method of effluent disposal is that
the precedent thereby established at any location would
make surface water discharge a readily—available option
for all other locations. This could happen even if poor
results occurred in the initial case, on the grounds that
water quality would not be lowered since it would have
been already polluted.
A second concern stems from the mobility in tides and
currents. Should unexpected pollution or other undesirable
conditions occur, nearby areas would be very easily
affected. Hilton Head Island itself could be "boomeranged"
by its own, or by others' effluent similarly discharged.
Thirdly, we note the sharp disagreement of other agencies
with EPA over the acceptability of discharging effluent
to our surface waters. When different agencies, each
charged with protecting public interests in the environment
reach such radically different conclusions, we think it
prudent to recommend against implementing a plan.
-8-
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The follov/inq quotations illustrate opposition to surface
water discharge of effluent. The statements are from
responses to the draft of South Carolina Coastal Council'
Special Area Management Plan for Hilton Head Island, datei
February 8, 1982. With regard to effluent, the Plan
recommended that:
"No discharge of treated effluent to the
surface waters around Hilton Head Island
should be permitted."
"Any solution for the disposal of treated
effluent should be comprehensive and should
include the entire island.
Responses to those recommendations included the following;
"The recommendations offered by the Coastal
Council in reference to both the discharge
of treated effluent and non-point source
runoff should be accepted and put into
effect as soon as possible.
Charles M. Bearden
S.C. Wildlife &. Marine
Resources Department
(letter of 3/12/82)
"The National Marine Fisheries^vice fully
supports the concepts put forth in this plan
for the protection of the resources on and
around Hiiton Head ™e" J™/™,,
extremely important to fishery resource^, ana
are quite fragile due to development pressures.
D. R. Ekberg
ii <5 Department of Commerce
(letter of 2/22/82)
-9-
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o: c •' f 1 ucnt o r. land, at a rate and by riot hods
consistent with the: absorptive capacity of the disposal
site, is far preferable to discharge to surface waters.
However, we believe that Hilton Head Island's problems
should be solved on Hilton Head Island. It is patently
unfair to pre-empt the use of off-island land from those
who may later require the use of that land. We agree with
the point of view, for instance, that Bluffton should not
become our septic tank.
We recommend that a site, or sites on Hilton Head Island
be acquired for effluent disposal, or that other methods
and technologies be explored. Among these could be:
1. Irrigation of roadsides, medians and/or
private property.
2. Recycling of purified water through the
potable water supply via aquifers and/or
storage tanks.
3. Anaerobic generators.
-10-
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June V.S,
Public Hearing on Environmental Impact Statement
regarding Wastewater Facilities for Hilton Head Island
W.L. Longnecker - Chairman, Island Concerns Committee;
Association of Sea Pines Plantation Property Owners
We found the wastewater facilities draft very informative and
accept the report as a good, comprehensive study of the problem on the
Island. We feel, however, that a decision on the recommended options
may be premature at this time.
Tnnue No. 1
First, the report emphasizes that the non-point source problem is the
most serious of the water disposal problems on this Island, to the point
that Federal Funding for any wastewater project is contingent upon the
correction of non-source runoff. The Section 208 study which is currently
being prepared is expected to recommend methods to control the non-point
source pollution and must be.integrated with the wastewater management re-
commendations before final decisions should be made.
Next, Island-wide coordination of all the wastewater management
programs is recommended. There is no platform yet to accomplish this. It
might be possible that considerable monies could be saved, and a better
u +. Issue No. 9
overall Island management would resuxc. u—
Third, having heard the proposals of the Sea Pines Public Service
District regarding the feasible program to upgrade the wastewater to
Lawton creek from secondary to tertiary water, I think that action justifi
a delay to allow measurement of the positive impact on,the system.
The additional spray irrigation and wetland recharge proposals are
important options to consider. The questions are which areas can be best
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-2-
benefited by spraying; how much actual usage can golf courses absorb;
and how much water can selected areas and wetlands take? If it is
feasible to reuse instead of dispose of the water, that is most
desirable and the long range saving of the potable water for future
generations is commendable.
Issue No. 4
A delay of action is normally not an acceptable decision. However,
in this case it might be advisable to delay a decision for a reasonable
period until the related facts are available; until more questions are
answered; and until important correlation is completed.
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HILTON HEAD ISLAND COMMISSION
POSITION PAPER - ENVIRONMENTAL IMPACT STUDY
This Commission, recognising that the EIS primarily is
a study of the Sea Pines Public Service District and its pre-
sent and future disposal of waste water, accepts the study
on its "face value" with certain exceptions. We feel that
the study and its proposals present environmental problems
and observations and offer solutions which do not fully answer
the total Island's future growth. Therefore, our acceptance
is one of acceptance of the study as a tool, a beginning point,
to further reconsider the problems presented. For example:
1. It points out the problem and importance of storm
water-run off as serious, but offers no real solutions.
2. The same concerning septic tank operations with re-
spect to non-point pollution.
3. Establishes "good areas" for septic tank operation...
..-."Slight" pollutant problems.
4. States that the 208 Studymust be adjunct to this
study, particularily the septic tank operations - but
this study is not completed at the present time.
5. Its waste water management and disposal proposals
seemed based more upon economic factors, than upon long
lasting impact.
6. It lacks serious treatment of the effect of waste
water disposal proposals on present potable water supply.
Basic observations of Study:
The non point pollution problem.
- Study points out that non point problem sources must be
controlled before Federal funding is available.
All nine (9) options for SPPSD effluent disposal fail
to take on the problem of non-point pollution.
- That the 208 Study concerning effective management practices
to abate non point pollution, is to be an adjunct to the EIS.
- That the OBERS criteria for projected population is, not
reflective of the Island trend-plus tourism.
Issue No. 2
- Broad Creek PSD growth to a capacity of~TTTTIjg^~~nT~l981 -
1983, then to a figure of 1.8 mpd in 1984. Where will this
effluent go?
- Discharge to the Sound, Ocean or Port Royal - fundamentally
sound, but does not resolve non-point pollution problem.
The septic tank operations and failures given minor/cursorv
rH snussion. A main NPP problem? "
Issue No. 11
- 1 -
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CONCLUSION - .'KOi'OiJALS:
1. The I-.'on point pollution problem is the most serious,
immediate environmental threat to the Island. 208 study
or not we propose the following:
a) Septic tanks -
At present, the only concern is that of Owners
when system backs up. Need to develope a monitoring
system and further, where PSD exists, develope program
to inspect, evaluate operations, then criteria for
time these units must go on line, (i.e. - years in
operation, faulty operation causing leakage or non
point pollution of adjoining/adjacent waters, etc.).
b) Storm Water Runoff -
Need to review status of 208 study. While we
know of no real program on-going in the U.S., there
must be some. Evaluate these. We point out that
the DSO amendments will contain requirements -for de-
velopers to develope run-off systems to handle the
first inch of water run off. As stated, we believe
this to be the major problem.
2. Effluent Disposal. Finally we are against those pro-
posals submitted, that offer open waters discharge into
Calibogue, Port Royal or the Atlantic. While the effluent
may meet all quality standards, we submit there are both
short-range and long-range problems.
a) Open discharge presents no curb on population
growth. Encourages development and should SPPSP receive
such approval, then PSD's all can.
b) Presents again no solution to NPP.
c) Has a negative effect on potable water usage.
One of our concerns, the study lacks attention to
our water reserves, their use and preservation. With
open water discharge, as opposed to irrigation, spraying,
flooding programs as proposed, all the good water
goes out to Sea and we will continue to pump some
70% for irrigation purposes as presently. Waste water
totals up to be 30% of water pumped. Why not save
30% of the 70% now being used for irrigation purposes.
Use for spray, golf irrigation, residential, farm,
business, industrial use, etc. -
*31
The real problem is again - population growth. Our conclu-
sion is basically that the rea1 population, growth, plus tourism,
far exceeds those projected in the study and far exceeds projected
build out programs.
- 2 -
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Finally, we urge that this study and whatever proposals
adopted, not be implemented too hurriedly. Those who are more
expert than we urge that time, not adinfinitum but 3-5 years
be given to refine the various proposals and explore alternative
techniques that exists and are not considered in the study.
On one hand we recommend serious programs to eliminate septic
systems which are high non point pollution sources. Forty
(40%) percent of Sea Pines is still on. septic. What then,
is the effect on the SPPSD capacity should we dash into this
proposal without further thought? What is the effect of the
"flooding" proposal? How fast may it be used as a partial
solution? SPPSD officials urge at least three years to determim
how much, or how little this technique may be used. What is
the total effect on final irrigation of all golf courses in
the SPPSD? Again, the answer is unknown until enough time
is taken to analyse the variables.
Therefore, let us use this Study as a tool, a resource,
to further study and resolve the unknowns it presents and
to coordinate such results in all phases for development -
building ordinances, land use plans, population projections,
Coastal Council studies, and others to follow.
- 3 -
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COMMENTS ON HILTON HEAD ISLAND ENVIRONMENTAL
IMPACT STATEMENT PRESENTED AT PUBLIC HEARING
ON JUNE 23, 1982
The Draft Environmental Impact Statement has considered a number
of alternatives for wastewater disposal. Through your review process
the list was narrowed down to five for which costs ranging from
$1.8 million to about $15 million were identified. These were:
Capital Cost
1. Lawton Canal Discharge w/Tertiary Effluent $ 1.77 million
2. Calibogue Sound Discharge w/Secondary Effluent $ 2.03 million
*
3. Rapid Infiltration w/Secondary Effluent $ 7.86 million
4. Spray Irrigation on HHI w/Secondary Effluent $14.93 million
5. spray Irrigation off HHI w/Secondary Effluent $13.83 million
During the three £lus years that the EIS has been in process,
the sea Pines Public Service District has continued to seek its
own ways to use and dispose of the treated wastewater. Some of
our efforts include:
1. continued spray irrigation on the Club Course and Shipyard Golf
Courses, and to construct new lines to spray irrigate the Ocean,
Sea Marsh, Harbour Town and the new nine hole course in Shipyard.
This will provide spray irrigation on Sh golf courses—all that
are located within the Sea Pines and Forest Beach Public Service
Districts.
2. Gained approval for pumping treated wastewater to the Forest
Preserve to re-establish a wetland. A three-year program will
be conducted to determine the quantity of water this wetland
-------
can accommodate. We will be pumping 600,000 GPD the first year,
1.0 MGD the second year and 1.5 MGD the third year.
We have conducted a study on the dispersion and environmental
impact of a secondary effluent introduced to deep water at the
southern tip of Hilton Head Island. We hope that we will never
have to construct an outfall in Calibogue Sound, but we have
felt the need to evaluate this alternative to a greater degree
than you have in the EIS.
Cubit Engineering from Clemson, South Carolina, performed
the study in March of this year and their report has been made
available to the EPA staff. The etudy has determined that there
would be no adverse impact on the environment from a 3 MGD dis~
charge at the southern tip of Hilton Head Island. In fact there
would be no change in background concentrations of any of the
parameters.
We have moved ahead with a treatment plant expansion that include
an environmentally sound method of sludge disposal. We will
be injecting the sludge into a sand media located at the treatmer
plant that has an underdrain collection system. The water remove
from the sludge will be pumped back to the treatment plant and
the sludge mixed with the sand will provide a top soil that
can be used for landscaping yards and flower gardens.
We have investigated actions taken by other communities in reusi'
treated wastewater. St. Petersburg, Florida, has treated their
wastewater with tertiary filters and disinfected to a degree
that health officials are satisfied that viruses have been kiHe<
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- 3 -
This process allows the City to use treated wastewater for
spray irrigation of golf courses/ parks/ road shoulders and
medians, and landscaping of individual yards as well as for
fire protection.
results of this EIS have significant importance to the Sea
Pines and Forest Beach Public Service Districts. In 1978 the Districts
received an order from the State Department of Health and Environmental
Control (DHEC) that required a study of wastewater disposal alterna-
tives. The EIS became that study. Within 90 days of the EIS com-
pletion, the District must submit an engineering report detailing
the concept for implementation of the. selected alternative. Within
270 days of approval of the engineering report, the District must
submit plans and specifications for construction of the facilities.
The facilities must then be constructed in accordance with a schedule
developed by DHEC. If the study is finalized as presented, we will
have no choice but to pursue the Sound discharge alternative.
There are a number of items in the draft EIS that give concern
to the District:
1. The draft indicates that some of the alternatives for effluent
disposal will allow the unbridled development of the Island.
• i pout an? service will only cause developers
We contend that denial of sewage service jr r
,. _ fro3<"pd wastewater on the Mainland*
to seek ways to dispose treatea
r3/-*n<=>. The added costs will then
This is in fact already being done. *»«
_ r ¦hn hp built to cover the increased
cause a higher number of units —
cost of sewage t~..™nt and disposal. The limits on development
densities should be handled by local ordinance and are presently
being pursued by the JPC and Beaufort County Council.
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The removal of the present outfall from Lawton Canal will not
open any of the closed shellfish areas. Water in the Lawton
Creek, Point Comfort Creek and portions of Broad Creek do not
presently meet SA standards because of runoff pollution. We
realize there would have to be a buffer zone for any outfall
from a treatment plant, but this buffer .zone falls between two
other buffer zones—those for Harbour Town and Palmetto Bay
Marina.
Federal funding for -any of the selected alternatives would be
limited to that portion of the work required to eliminate the
present outfall. This funding wotald be used to assist present
customers and would not be used for plant expansions for new
development.
The EIS, however, prohibits any Federal funding unless a
storm water runoff program is implemented for Sea Pines and
Forest Beach. Neither Public Service District has authority
to work in this area and it is questionable as to the program
that could be implemented. I say this because all work done
by the 208 study and by the Coastal Council, as well as the
JPC's development standard ordinance, deals with runoff for
new development. None of these seem to have a solution for
runoff pollution for developed areas such as Sea Pines and Forest
Beach.
We raise the question: Does EPA have a suggested program
for controlling or treating runoff from developed areas? If
you were given the responsibility to stop contamination of oyster
beds, what reasonable action would be taken?
-------
- 5 -
Issue No. 4
The Sea Pines and Forest Beach Public Service Districts feel
there is considerable study still needed to insure that treated
wastewater is used to its maximum. We have a limited amount of
good drinking water and it is being used in great quantities for
non-potable purposes.
Our plan is to do the following:
1. Continue the three-year program on the wetlands recharge and
work to gain more land in the Forest Preserve. Recently there
was some land given to the Island Audubon Society by Mr. Don
Schrader. This land and other tracts may be available for water
recharge.
2. Monitor the water used on the present and new golf courses to
see how much water each is using and work with golf course super-
intendents to try to maximize use of the treated wastewater.
3. Pursue the use of tertiary effluent for spray irrigation through-
out Sea Pines and Shipyard. The construction of water mains
to the five golf courses provides a delivery system for spraying
5§
treated wastewater on landscaped areas similar to the system
3
^ used in St. Petersburg, Florida. We know "that great quantities
of potable water are used for these purposes, but we need to
quantify this use and see how much treated effluent could be used.
4. We would like to install tertiary filters as soon as possible
so that the best quality water can be provided for spray irri-
gation, and that any continued discharge to Lawton Canal will
meet limits of 5 mg/1 for both BOD and suspended, solids. This
plan is in fact one of the alternatives discussed in the EIS.
-------
- (> -
5. By providing a tertiary degree of treatment, we would then ask
to have the limits of discharge removed so that the Districts
can proceed with meeting their obligations to serve.
It is necessary to lift the limit on the amount discharged
to Lawton Canal in order to serve the vacant lots within the
developed subdivisions and to serve the areas presently on septic
tanks. (Currently there are 906 houses in Sea Pines still on
septic tanks or 37% of all houses in Sea Pines.)
6. At the end of a reasonable time, see if we can accomplish a
zero discharge. This is our desire—to have a 100% reuse of
the wastewater. We would also like to see if County Council
and the Coastal Council are able to make any progress in improvin
the existing water quality in Lawton Creek and Broad Creek.
7. If at the end of the designated period we have not obtained
a zero discharge and if progress has been made in eliminating
the non-point pollution from the developed areas, we would then
pursue the other alternatives allowed in the EIS.
We ask your consideration in writing the final EIS in such a
way that the program I have outlined be classed as an acceptable
alternative to EPA.
-------
Commissioners
Newton A. Lieurance, Sr.
Chairmen
Leslie M. Bernick
Robert E. Huber
Carl H. Lind
James L. Rowe
Broad Creek
Public Service District
P.O. Box 5628
Hilton Head Island, South Carolina 29938
June 14, 1982
803-785-1104
William T. Hunt«r
Manager
Mr. E. T. Heinen, Chief
Environmental Assessment Branch
Environmental Protection Agency
Region IV
345 Courtland Street, N.E.
Atlanta, Georgia 30365
RE: HILTON HEAD ISLAND, SOUTH CAROLINA
ENVIRONMENTAL IMPACT STATEMENT
Dear Mr. Heinen:
Issue No. 2
Issue No. 9
We have previously expressed deep concern with the population
and flow projections contained in the Draft Environmental Impact
Statement (EIS) and we herewith reiterate that concern. We
fully realize that the OBERS-based population projections must
be used to evaluate alternatives. However, by so doing, considera-
tion of alternatives for the majority of the Island has been
almost totally disregarded. In essence, the EIS presents an in-
depth study of alternatives for the two public service districts
which provide service for approximately thirty percent of the Island
But these two districts presently have about fifty percent of the
Island's population and also have the most critical wastewater
treatment and disposal problems. However, it seems incomprehensible
that potential problems and solutions for the remaining seventy per-
cent of the Island would be so blatantly disregarded by using popula>
tion data that is obviously erroenous. If, as purported, the EIS
is applicable to the entire Island, alternatives available to all
PSD1s and Non-PSD areas should be evaluated and the preferred alter-
native (s) described.
Attached hereto are copies of previous correspondence, none of which
has been acknowledged by EPA but all of which express our concerns
about the EIS.
Very truly yours,
B^OAD CRE13K PUBLIC SERVICE DISTRICT
William T. Hunter
Manager
WTH:eh
Enclosures
-------
Commissioners
Zack J. Van Landlngham
Chairman
Carl H. Und
Newton A. Lieurance. Sr.
Broad Creek
Public Service District
P.O. Box 5628
Hilton Head Island, South Carolina 29938
MX
803-785-1104
William T. Hunter
Managar
August 20, 1981
Mr. Charles Jeter, Regional Administrator
Environmental Protection Agency
Department of Natural Resources
Region IV
345 Courtland Street, N.E.
Atlanta, Georgia 30308
RE: HILTON HEAD ISLAND
ENVIRONMENTAL IMPACT STATEMENT
Dear Mr. Jeter:
Issue No. 2
On several occasions within the past nine months, Broad Creek
Public Service District has expressed its deep concern with
the population and flow projections contained in the Environ-
mental Impact Statement. The question was asked of Mr. Robert
Cooper on December 9, 1980, if the projections shown in the
EIS would be interpreted as being limitations. Mr. Cooper con-
firmed that the OBERS population projections are utilized in
allocating EPA funds and funds will not be granted to any project
if the actual populations is in excess of the OBERS population.
The EIS indicates that the peak monthly average flows for the
year 2000 for Broad Creek Public Service District based on
OBERS is 0.64 MGD.
This value is extremely low inasmuch as the actual peak monthly
flows at the Broad Creek Public Service District Plant are
approaching 0.6 MGD at this time. As a matter of record the
South Carolina Department.of Health of Environmental Control has
issued a conditional construction permit to the District to double
the capacity of the treatment plant to 1.2 MGD. This contract has
been awarded, construction has started and will be completed by
April 1, 1982.
Undoubtedly some of the other public service district of Hilton
Head will also be experiencing this same situation. This places
everyone at the distinct economic disadvantage because it precludes
the potential of receiving EPA Grant Funds to offset part of the
construction costs. Inasmuch as the OBERS population is obviously
incorrect because the actual population and flows will in 1983 exceed
the PBERS population projection for the year 2000, it is respectfully
requested that EPA review this information and take whatever steps as
-------
Mr. Charles Jeter
Page two
August 20, 1981
The District is also very disturbed by the connotation of "no
action" in the Draft EIS. Broad Creek Public Service District
has a history of providing wastewater treatment facilities IN
anvanrF nf the need thereby precluding the discharge of effluent
not^in accordance with. ^Department of Health and Environmental
fontrol standards. Unlike others, we take pride in providing
adequate capacity before it is needed rather than waiting until
plant capacity is SSSiided before starting «e therefore object
to any inference that no action is being taken and respectfully
request that this terminology be corrected.
Very truly yours,
BROAD CREEK PUBLIC SERVICE DISTRICT
\ V
'~\ \YJU
„/Vw \
William T. Hunter
Manager'
WTH:eh
cc: BCPSD Commissioners
Hussey, Gay & Bell
Cary Griffin
-------
June 16, 1981
i§
Q)
3
CO
H
Mr. Robert Cooper
Environmental Protection Agency
EIS Project
345 Courtland Street, N.E.
Atlanta, Georgia 30308
RE: BROAD CREEK PUBLIC SERVICE DISTRICT
HILTON HEAD ISLAND, SOUTH CAROLINA
Dear Mr. Cooper:
Enclosed is a copy of the 10-year plan as adopted by the
Commissioners of the Broad Creek Public Service District.
This plan indicates the projected population and capital
improvement projects necessary to provide services to the
area within the public service district.
As have mentioned to you on several occasions, the
District is particularly concerned about the population
and flow projections contained in the EIS. In addition,
we are concerned about the various effluent disposal
alternatives which are being evaluated for Broad Creek
Public Service District and for other districts on the
island.
In a recent article in the "Island Packet" we noticed that
the .draft EIS has been submitted to the EPA and is under
review. We would appreciate very much the opportunity to
discuss this draft with you and will be happy to arrange
to meet you in your Atlanta office. We would also re-
quest that Ms. Louise B. Franklin and Mr. D. Randolph
Grubbs be requested to attend this meeting in order that
we could have the benefit of their input.
-------
Mr. Robert Cooper
June 16/ 1981
Page 2
Please let us know when it would be convenient to meet
with you.
Sincerely,
LONNIE E. DYE, P.E.
LED/jdt
cc: Mr. Bill Hunter
Mr. Mike Jordan
Ms. Louise B. Franklin
Mr. D. Randolph Grubbs
Enclosure
-------
Commissioners
Zack J. Van Landlngham
Chairman
Carl H. Llnd
Ntwion A. Uavranca, Sr.
Broad Creek
Public Service District
P.O. Box 5628
Hilton Head Island, South Carolina 29938
803-785-110
William T. Hunt
Managar
TO:
FROM:
DATE:
SUBJECT:
Distribution
William T, Hunter
May 5, 1981
TEN YEAR PLAN
Enclosed is the final plan which has been modified to include
some capital imput from Hussey, Gay & Bell.
The important points to consider while digesting this are:
Units. The master plan for the Zone II property has not been
developed; therefore, the number of units included (1,560) was
an "off the wall" guess.
Timing. The timing of developing property for sale or for
improvements on existing lots is pure conjecture at this time.
We followed a consistant ten year plan which resulted in 100%
developed and improved property by 1991.
This is a sliding scale control and by slowing down or speeding
up will affect expansion and income accordingly.
Dollars. All income and expenses are shown in today's dollars
with no consideration given for inflation. At best we would hope
that they (income and expense) would offset each other.
Debt. No provision was given for additional debt but the amount
to be funded is evidenced by the accumulative negative cash positic
in years 1982 thru 1988.
Replacement. $75,000 per year has been set aside for replacing
existing facilities. This is an arbitrary amount and could easily
be double this.
-------
Operating Expenses. We show a nominal increase each year of
-50,000. Over the ten year period this would result in dmihi,™
the 1981 operating costs. doubling
WTHseh
Distribution: Zack J. VanLandingham
Newton A. Lieurance, Sr.
Carl H. Lind
Gus Bell
Lonnie Dye
Cary Griffin
William T. Hunter
-------
BROAD CREEK PUBLIC SERVICE DISTRICT
USAGE/REVENUE
April 30, 1931
Single Family
Fixed - 95 units @ $20 per month
Metered - 149 units @ $25 (average) per month
$ 22,800 Annual
$ 44,760 Annual
New homes are being processed at ten per month. For this
projection we will use 100 units per year tapping into the
system.
Availability - 767 units @ $108
Total Single Family
As of November 1, 1981 everyone will be metered and
the user income will increase in most instances.
At 12/31/81 we should have the following inventory:
295 Metered hours @ $25 per month
30 Under construction
686 Unimproved
1,011 Total
$ 82,836
$ 150,336
$ 88,500 Annual
lulti-Family
Fixed - 589 units @ $20 per month
Metered - 380 units @ $25 per month
Under construction - 128 units
At 12/31/81 we will have 1,097 metered condominiums
1,097 @ $25 per month
Commercial
$ 141,360 Annua!
114 ,000
$ 255,360
$ 329,100 Annua
Present billings average $150,000 per year but next year we
have deleted the PDR irrigation of Queen's Folly -- about $6,000
The fixed charge to Outdoor Resorts has been deleted also.
-------
SUMMARY
The annual billing as of January 1, 1981:
Single Family
Metered $ 88,500
Availability 74,100
$ 162,600
Multi-Family
Metered $ 329,100
Commercial § 150,000
Millage $ 38,000
Total $ 679*,700
User revenue includes 1,392 units 8 $5 (excess) x 12 months » $ 83,520
-------
NEW CUSTOMERS
Single Family
One-third of the applications have been for the Inverness
Section. Based upon 75 completed houses per year, we would
experience the following:
Units Amount Cost Per Tap
*
Mariner 50 $750 $1,000
Inverness 25 $750 $ 100
75
Summary:
Revenue - 75 @ $750 $ 56,250
Costs
50 8 $1,000 50,000
25 0 $100 2,500
$ 52,500
Net Income $ 3,750
Actually with the build-up starting to happen in Mariner,
we are now experiencing houses being constructed next to
existing homes; herefore, tapping into'existing tanks
with only about $100 costs.
Multi-Family
The master plan is not complete for the Zone II property
and we cannot determine the yearly or ultimate building
rate.
Zone III- Marina property along the west side of Highway 278
will probably experience the following:
1400 multi-family units over a 7-10 year period.
Construction will start in 1981 and should result in
at least 140 units connecting each year.
Following the density/available property thesis in Zone III,
we could realize the following:
Total acres 430
Golf course 150
Other 20
Net acres 260
-------
Density - sixty an acre =1,560 units
Over a ten—year period will result in 156 units per year.
Summary 296 units per year
Commercial
There should be no commercial in Zone II, but there are
plans for 300,000 square feet of commerciai/retail/office
in the Marina property.
Developed over a five-year period will result in 60,000
square feet being completed each year.
Other
No consideration has been given to expansion of District
boundries to the north or south.
It is assumed that the present Long Cove customers will be
transferred to Sea Pines PSD before the next fiscal year.
However, there are some out parcels which are completely
surrounded by BCPSD and we should include them in our
contingency plans.
EGR Property - 3h acres - 26,000 square feet retail
Mr. Mack - 1*5 acres - unknown
Washington Tract - 50 acres - ^ppJyin;LaQn»ablf_acres
* factor of 90% - 45 acres
and a density of six to the
acr6 would result in 270 units,
Summary of ultimate build-out.
Present property owners amily
^ 1,097 multi-family
„ TT 1,560 multi-family
Zone III 1-/400 multi-family
Total 5,06 8 units
Commercial
Present - one 360 room hotel
40,000 square feet commercial
Addition - one 324 room hotel
300,000 square feet
Other
"26,000 square feet
rTA *
-------
i-iay ^ / , x 3 O X
PALMETTO DUNES RESORT
ZONE II
Undeveloped
Tract
AC
Type
Density
Per Acre
Total
Units
GPD
Unit
Total
Flow
1
4.7
Villas
12
56
300
16,800
2
6.7
Villas
12
81
300
24,300
3
4.0
Beach Club
—
—
—
10,000
4
6.5
Villas
12
78
300
23,400
5
6.4
Villas
12
77
300
23,100
6
7.8
Villas
12
94
300
28,200
7
9.6
Villas
12
115
300
34,500
8
12.2
Restaurant
Hotel
600
34 0 Room
34 0 Room
50
100
30,000
34,400
9
11.6
Villas
8
93
300
27,900
10
6.15
Villas
8
49
300
14,700
11
5.2
Villas
8
42
300
12,600
12
4.4
Villas
8
35
300
10,500
13
1.6
Residential
—
8
300
2,400
14
3.35
Lots
—
17
400
6,800
15
16.9
Lots
—
45
400
18,800
16
4.6
Lots
—
12
400
4,800
17
3.35
Lots
—
8
400
3,200
18
10.4
Lots
—
24
400
9,600
19
7.2
Lots
—
19
400
7,600
20
5.0
Lots
i—
24
400
9,600
21
8.9
Office/Park
w —
400
20,000
875
372,000
-------
USAGE
(1) Present Demands
1,392 units 0 350
Hotel/Commercial
487,200 gallons daily
100,000
Total Present
587,200
Reserve
716 unimproved lots 8 350
Total Committed
250,600
837,800 gallons
Proposed Construction
(2) G.E. Parcel
Mariner Inn
{3) Marina Site (Zone III)
1,614 units
300,000 Square Feet
Total Zone II
Total known committment
(4) Zone II
877 units
100,000
100.000
200,000
454,500
157,100
611,600
1,627,800
372,000
(5) Non-District
Commercial
270 units 0 350
10,000
94,500
104,500
Total potential capacity required - 2,125,900 gallons per 4ay.
-------
Pod
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
26
27
28
29
30
31
32
33
34
35
36
37
38
39
40
May 27, l&bl
PALMETTO DUNES RESORT
ZONE III
Description
Residential
Residential
Yacht Club
Residential
Residential
Residential
Residential/Commercial
Residential/Commercial
Residential/Commercial
Racquet Club
Bank
Transportation Hub
Post Office.
Tour Bus Depot
Island Villa Rentals
Chamber of Commerce
Commercial
Restaurant
Residential/Commercial
Residential
Residential
Mall-Commercial
Bandshell
Church
Church
Residential
Commercial
Commercial
Commercial
Racquet Club
Bazaar
Residential
Residential
Maintenance
Marina Spoil Area
Residential
Service Center
Commercial
Restaurant
P.D.R. Signage
1 BR. 2 BR. 3 BR.
units units units
no. no. no.
28
240
16
20
15
8
28
38
64
58
21
112
52
68
38'
20
24
20
16
125
59
79
123
58
45
12
10
100
11
13
35
50
TOTAL FLOW
536 839 239
107,200 251,700 95,600
Commercial
4 ,800
2,500
2,840
1,900
22,500
200
500
500
150
500
250
4,600
21,500
1,640
16,000
0
1,050
1,200
4,000
6, 600
3,200
25,000
1,000
1,500
0
3,600
4,600
25,000
0
157,130
157,130
Total 611,630 gallons
Total 1.614 «*¦*•?+• a
-------
.• ' i«r»' y" I *. -»• •; •,|H'
Ct•• t i.\v.i i ¦ M.r a.>
May 18, 1981
Mr. Robert Cooper
Environmental Protection Agency
E1S Project
345 Courtland Street
Atlanta, Georgia 30365
BROAD CREEK PUBLIC SERVICE DISTRICT
Hilton Head Island, S.C.
CVJ
!§
a
CO
i®
H
Dear Mr. Cooper:
Ias we discussed on May 4th, the Broad Creek Public Service
[District is very much interested in the E1S for Hilton Head
Island. The District is particularly concerned about the
(population and flow projections contained in the E1S. In
{additionwe are concerned about the various effluent dis-
posal alternatives which are being evaluated for BCPSD and
cor other districts on the Island.
On behalf of the District, we respectfully request an
opportunity to discuss the draft E1S at the earliest possible
date in your office. Please let us know when we can meet.
Yours/Jvery truly,
LONNIE E. DYE
gdg
cc: Bill Hunter - BCPSD
Mike Jordan
Claude Terry & Assoc.
Gannett, Fleming, Corddry & 'Carpenter
-------
Commissioners
Zack J. Van Landingham
Chairman
Carl H, Lind
Newton A. Lieurance, Sr.
Broad Creek
Public Service District
P.O. Box 5628
Hilton Head Island, South Carolina 29938
June 11, 1981
803-785-1104
William T. Hunter
Manager
Mr. Lonnie Dye
Hussey, Gay & Bell
P. 0. Box 14247
Savannah, Georgia 31406
Dear Lonnie:
Regarding the next set of documents 2nd meetings to be set
up by ESI/EPA, we still feel that it is imperative to present
them with correct and current data.
Mike Jordan and I feel that a face to face meeting with the
people involved would be necessary and important but at least
you should submit to them the Ten Year Plan as adopted by the
District.
This would verify our dispute with their low estimate of users
and required flows. In addition, we want to go on record as
stating our position concerning the ability to dispose of
effluent with the same options they are recording for the other
Districts on the Island.
Thank you.
Very truly yours,
BROAD CREEK PUBLIC SERVICE DISTRICT
( v \\
'..V :vv\
William T. Hunter
Manager
WTHreh
cc: R. C. Onorato
Gus Bell
Cary Griffin
Mike Jordan
-------
CHAPTER V
EIS COORDINATION
-------
CHAPTER V - EIS COORDINATION
PART A. INTRODUCTION
Public participation programs are mandated by Federal Regulations
governing the preparation of Environmental Impact Statements. Public
participation is an important and valuable part of the EIS process
because it provides for active public involvement in developing and
evaluating wastewater management programs.
At the beginning of the Hilton Head Island EIS, a public partici-
pation program was established to provide opportunities for interested
groups/individuals, and government agencies to participate in the
development of the EIS. A Review Committee was established to serve
in an advisory capacity to EPA and their consultants through a series
of committee meetings held during the EIS preparation. In addition,
two public meetings and a public hearing were held at various stages
in the process, a£d interested agencies and groups were asked to comment
on the Draft EIS.
A complete list of the agencies and interest groups who were
involved in the public participation program is presented below.
PART B. AGENCIES AND GROUPS
Public Agency
Beaufort County Council
Beaufort County Joint Planning Commission
Department of the Air Force
Department of the Army Charleston District Corps of Engineers
Department of the Army Savannah District Corps of Engineers
Hilton Head Island Commission
Low Country COG
S. C. Coastal Council
S. C. Dept. of Health S Environmental Control
S. C. DHEC, Shellfish Division
S. C. Wildlife § Marine Resources Department
U. S. Department of the Interior - Office of Environmental Project Reviev
U. S. Public Health Service
Public Service Districts
Broad Creek PSD
Forest Beach PSD
Hilton Head No. 1 PSD
Sea Pines PSD
-------
Homeowners Associations
Association of Land Owners of Port Royal Plantation
Association of Sea Pines Plantation Property Owners, Island Concerns
Committee
Association of Sea Pines Plantation Property Owners, Inc.
Forest Beach Community Association
Palmetto Dunes Property Owners Association
Shipyard Plantation Property Owners Association
Spanish Wells Property Association
The Hilton Head Island Community Association, Inc.
Private Groups
Audubon Society
Beaufort/Jasper County Comprehensive Health Program
League of Women Voters, Hilton Head Island Members-At-Large Unit
May River Committee
N.A.A.C.P., Hilton Head Chapter
Hilton Head Fishing Cooperative
Shellfish Interests
Sierra Club, Nancy Cathcart Group
Sierra Club, South Carolina Chapter
Developers
C and S Investments South
Heritage Properties
Hilton Head Company
Hilton Head Plantation
Palmetto Dunes Resort
Sea Pines Plantation Company
Trade Associations and Business Groups
Chamber of Commerce
Council of Architects
Hilton Head Hospitality Association
Home Builders Association
Private Citizens
Thomas Barnwell
Emory Campbell
Charles Go1son
M. T. Laffitte
L. P. Struble, Jr.
Leslie Teal
V-2
-------
CHAPTER VI
LIST OF PREPARERS
-------
CHAPTER VI - LIST OF PREPARERS
Project Personnel
U. S. Environmental Protection Agency
Robert B. Howard
Robert C. Cooper
William J. Patton
Chief, EIS Preparation Section
EIS Project Officer
Chief, S.C./Tenn. Facilities Planning Section
Consultants
Gannett Fleming Corddry and Carpenter, Inc.
Thomas M. Rachford Senior Project Manager
D. Randolph Grubbs Project Manager
L. Edward Stom Project Engineer
Kenneth E. Vinson Assistant Project Engineer
Paul Andre DeGeorges
John W. Jacobs
Environmental Scientist
Environmental Scientist
Claude Terry & Associates, Inc.
Claude E. Terry
Louise B. Franklin
Robert J. Hunter
Thomas C. Mather
Project Executive
Project Manager,
Environmental Planner
Environmental Scientist
Environmental Scientist
VI-1
-------
APPENDIX A. SOUTH CAROLINA COASTAL COUNCIL - HILTON HEAD
ISLAND SPECIAL AREA MANAGEMENT PLAN
-------
Special Area Management Plan
for
Hilton Head Island
South Carolina Coastal Council
1982
ENVIRONMENTAL IMPACT STATEMENT
BRANCH
ar?nn nr? -
MAY 12 1982
iiD\snns
REGION IV • EPA
-------
HILTON HEAD ISLAND SPECIAL AREA MANAGEMENT PLAN
April 23, 1982
South Carolina Coastal Council
-------
Table of Contents
Page
Chapter One - Introduction . 1
Chapter Two - Water Quality ...... 2
I. Treated Effluent Disposal . 2
A. Issues 2
B. Existing Policies, Rules and Regulations . 3
C. Management Policies ... 4
II. Storm Water Runoff 4
A. Issues ........ ..... 4
B. Existing Policies, Rules and Regulations 5
C. Management Policies 6
Chapter Three - Tidal Wetlands 7
A. Issues ........ 7
B. Existing Policies, Rules and Regulations . 8
C. Management Policies 14
Chapter Four - Freshwater Wetlands 16
A. Issues 16
B. Existing Policies, Rules and Regulations 19
C. Management Policies 20
Chapter Five - Beaches and Dunes 21
A. Issues 21
B. Existing Policies, Rules and Regulations ... 22
C. Management Policies 25
Chapter Six - Public Access 26
A. Issues Z6
B. Existing Policies, Rules and Regulations ... 26
C. Management Policies 27
Chapter Seven - Cultural Resources 28
A. Issues 28
B. Existing Policies, Rules and Regulations ........ 28
C. Management Policies 30
Appendix A - Recommended Strategies for Storm Water Management
Appendix B - Maps (to be printed at a later date)
-------
CHAPTER ONE
Introduction
Hilton Head Island is recognized internationally for its unique barrier
island environment that provides the atmosphere for a variety of recreational
activities. That Hilton Head Island plays a major economic role in the state's
tourism industry, is of important significance. Its importance to the local
economy is also obvious. However, in recent years the predictable rush to
maximize the development potential of the island has caused concern over long
term implications for the natural environment, public resources, and the
stability of its economy.
The current year round average population is approximately 14,000.
Current peak population counts, however, surpass 40,000. According to local
and regional estimates, those figures will increase to 35,000 and 100,000
respectively as parcels that are already master planned develop. Considering
the large tracts of land that are not currently master planned, the development
potential of those areas, predictions for a "buildout" scenario are 70,000 and
150,000 respectively. Certainly a number of unknowns could affect these
estimates, but based upon the best available information and current economic
trends, they are not unrealistic.
Current population and development has created an assortment and varying
degrees of environmental problems. It should follow that multiplication of
these figures buy two or three times will compound any existing problems unless
some mitigating measures are implemented. It is on the basis of these
assumptions that the following policies are established by the South Carolina
Coastal Council in the form of a Special Area Management Plan for Hilton Head
Island. These Policies pertain only to new projects or the expansion and
significant alteration of existing projects and activities.
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CHAPTER TWO
Water Quality
I. The discharge of treated savage into the surface waters of Hilton Head
Island.
A. ISSUE: The discharge of treated sewage is currently, and will
continue to be, an issue for developers and residents on Hilton Head
Island. A preliminary draft of the Hilton Head Island, S. C.
Environmental Impact Statement has approved three alternatives for
discharge: 1) land application on Hi Leon Head Island, 2) land
application off the island, and 3) discharge into Calibogue Sound.
The EIS addresses only the needs of the Sea Pines PSD.
Discharge into Calibogue Sound has four primary points for
discussion.
1. Where (depth, tidal flushing, etc.)
2. Method (discharge $ treatment)
3. How much (gallons per day, limited, unlimited or none)
4. How long (temporary solution or permanent)
While all of the above points are important, determining hew
much, if any, discharge is probably the critical point. First, it is
the consensus of the staff that limiting the amount of discharge may
be possible for a short-term period; however, the demand by other
PSD's may be too difficult to withstand once the precedent for the
island is set. This precedent could certainly involve Port Royal
Sound in subsequent years. The EIS does not investigate a solution
for an island-wide problem, but does pose serious implications for
inevitable demand.
Second, the disposal of treated effluent into Class SA waters
may set a dangerous precedent. The pressure to discharge sewage
effluent along the coast continues to grow. It should be noted that
surface-water discharge is, in most cases, the least expensive method
and thus attractive to most large-scale developments.
Third, there are existing and accepted practices, philosophies,
ana guidelines that should be considered when reviewing this problem.
References to the Clean Water Act and its objectives should be
considered. Existing South Carolina Coastal Management Program
policies should be considered (.see existing policies section :or a
detailed discussion). Past Coastal Council actions should be
considered (e.g., Carolina Water Service application to discharge
into the Stcno *iver). Finally, consideration should be given to the
possible, and probable, environmental effects to marine resources
"(e.g., shellfish, etc.), to include assessment of cumulative impacts.
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3. feriatin* Policies. ^uleg. Regulations, and "Stata of the Arcs"
M-namgs:
m-tnt* 1 TMft-nt Plan (III-35, 1 d) Wastewater discharges
shoula be locate* waere uiey pose che least ecological threat - in
areas where disruption or wetlands can be avoided, in areas with good
tidal flushing, and along water courses with relatively low water
quality classification.
rn«ra7 \fena«s«nt Plan (III-30) Other than actual location of
facilities m sensitive tueas, the major negative impact associated
vith sewage treataent systems is the potential water quality
degradation from effluent discharge.
Mmuemt Plan CIXI-SX, 1 a) Swage treataent
fadliaea ana crausmsiiui "systsoa «ust meet applicaole federal,
stats and local wear quality standards.
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Secondarily treated effluent also contains nutrients such as
nitrogen and phosphorus that serve as limiting factors for primary
producers. Subtle changes in concentrations of these nutrients cam
result in changes of types of primary producers, causing shifts in the
species composition and abundance of the entire estuarine community.
C. Policies
1. No discharge of primary or secondarily treated effluent into the
critical areas of Hilton Head Island. This recommendation does not
preclude the evaluation of ocean discharge or any other innovative
technologies found to be acceptable by the South Carolina Coastal
Council. In the event that an ocean discharge is found to be
acceptable, the S. C. Coastal Council will consider the location of
the discharge at the most appropriate location.
2. Any method of effluent disposal, other than land application on the
island, will be evaluated on the basis of a comprehensive island-wide
solution to the short and long term requirements of Hilton Head Island
and the surrounding natural systems.
3. In view of the critical future potable water requirements for Hilton
Head Island, and the fact that little information is now available
concerning present use, quantity and quality of the existing ground
water, the S. C. Coastal Council recommends that the appropriate
parties undertake comprehensive studies to determine the quantity and
quality of potable water resources for Hilton Head Island to
accommodate future growth predictions.
II. The discharge of storm water runoff into the surface waters of Hilton
Head Island.
A. ISSUE: The most serious existing threat to the surface water quality
around Hilton Head Island is from storm water runoff or, as it is
often referred to, nonpoint-source pollution. Without exception, the
volume and substance of this discharge is a function of development,
especially in a rapidly urbanizing area like Hilton Head Island.
While general water quality on the island is not a major problem at
this time, there are significant "trouble spots" on the Island.
Assuming a continued growth pattern, these "spots" can be expected to
broaden significantly ana to begin a transition from short-term
occurances to long-term or even permanent problems. Areas expected to
receive the greatest impacts are Lawton Canal, Baynard Creek, the
Folly, Fish Haul Creek and, most importantly, Broad Creek.
Given existing development guidelines these waters will likely
face a reduced capacity to assimilate increased amounts of runoff and
will likely meet only SB or, in some cases, SC water quality
standards.
This situation would have serious implications for the shell-
fishing industry, the recreational use of wetland areas, and the
natural environment which is an essential part of the atmosphere and
ambience of Hilton Head Island. Certainly when the expected volumes
of storm water runoff occur in combination with possible discharges
of treated effluents, serious water quality issues will occur that may
effect the public health, marine resources, public uses, and the
economy of the area.
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3. Existing Policies, Rules. Regulations, and "State of the Arcs"
findings:
Coastal Management Plan (III-17, 1 d) Drainage plans and
constructm«*!'<"ras gor residential development shall be designed so
as to control erosion and sedimentation, water quality degradation,
etc. Example techniques include buffering and filtering runoff, use
of permeable paving surfaces, detention ponds, etc. Best management
practices designed co control nonpoint-source runoff that are
developed as part of 208 Water Quality Planning also apply to new
housing projects.
fo»«rai Managqnent Plat (111-22, I d) Oca should b. taken in
pv-U m mnimi~dlrecT drainage of roadway runoff into
adjacent water bodies.
Plan OII-27,lb)
facilities must oemunstracewmpliance with applicable Federal and
state water quality standards, specifically those addressing drainage
and discharge of storm water runoff.
Management Plan (III-40, 1 d) Drainage plans and
consi^^T^Tor^Se«iaI~developiiMtstoi^d bedesiged to leMen
„ ---cinn water quality degradation and other negative
filtering runoff, use of
woiutad buffers, etc. Best Management Practices developed
STpart Sf t£e irea-vri.de 208 Water Quality Plan should be implemented
through the management of major new eomaercial developments.
r—1 s*ma
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C. Policies
1. The direct discharge of untreated storm water runoff into the critical
area (as defined by the S.C. Coastal Zone Management Act) shall not be
allowed.
2. The South Carolina Coastal Council shall utilize "Best Management
Practices", such as those identified in the Hilton Head Island 208
Water Quality Study, in the review and issuance of permits and
certifications. The "Best Management Practices" will be applied on a
project by project basis as warranted by specific requirements.
(See Appendix A.)
3. Optimum utilization of marshes and freshwater wetlands for filtering
storm water runoff should be required.
4. Drainage projects shall be designed so that the final elevation of a
storm water discharge outlet is at or above the elevation of the
receiving critical area, unless no feasible alternatives exist.
5. An SA, or better, water quality classification shall be maintained or
achieved in surface waters surrounding Hilton Head Island.
6. It is recommended that the South Carolina Department of Health and
Environmental Control (DHEC) consider regulating specific point source
discharges of storm water via the National Pollutant Discharge
Elimination System (NPDES).
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CHAPTER THREE
Tidal Wetlands
marinas);and the discharge of treated effluent and non-point source
pollutants.
a TCC7TP• rw,« rn the raoid and continuous development taking place on
mfe Head IslSd.TrMSwe exists for filling, dredging, spoil
"?iMn , water access facilities and the discharge or
treated eflluent^nd non-point source pollutants. While protection
^ S mn.1- A1T9CT adverse impacts is afforded tidal wetlands through
of the^astal Council and the U.S. Any Corps
rfPnriMers significant pressures to alter these areas will continue
of B^ineers, signi „Lsa o£ development and through projected
auring the teowi plmned pnase o ^ fae ^
^ ^ **3* »¦**« ««
J _?Tjn?n? lH 71 hm areas such as isolated marsh hammocks to which
SSicSTL^s SnlHaiS only by filling or bridging. Kater
'I-.,. r0 these sites will also cause increased applications for
Sarins activities and their accompanying spoil disposal sites. The
c-eeks through dredging will, in many cases, result in
^ilStiOT problems and the need lor periodic rainwnance dredging.
Develoners are finding it difficult to provide highland spoil disposal
sUwfSd 1?i "certain that pressure to use non-vegetated wetlands
(mudflats and non-vegetated creek edges) as disposal sit« will occur
during future phases o£ development.
1 f-MMdna oressure is beginning and will continue to be felt
for the^SSrSetion of marinas. A trend toward lock system/basin type
. . . -0 flTjrjear. The results o£ this phenomenon will be
SU2? «cSf ™??e 2a«r1or boaters and home owners accompanied by
V "cMn *» ^ »d
adjacent natural creeks into which they empty.
4. mUAm rh»v* swears to be no overriding justification for
the b^if rme mriS inl^S^ i»P"ving the functions associated
•1.1^ .i?l,™ staff assumptions are that the scarcity of large
S£,fSf SSfrint property and the desire for additional waterfront
devel ocment sites are the prim ^iv.srorttus shift from the more
traditional approaches to manna developments.
» 4irs-r iaoact of marina develoanent is the closure of shellfish
grounds within iMO feet of the site asa pr gramr
5 - j i... .mnT rrsnds sufgest a demand tor approximately lu
^^r?S TSlton Head Island. That situation combined -with water
, ,T, associated with storm water runoff, and wastewater
dilcharses cauld eliminate shellfish grounds as a resource for public
a road Old House, Jarvis and Skull Creeks are the most
fiSiv^reas of imcact. What kind of balance can be obtained between
Lhe d«an?for marinas and the shellfish resource? It is predictable
that ^e resource will be eliminated as a direct result of competing
uses that carry acre economic weight.
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The discharge of created effluent into surface waters is and will -
continue to be a major issue on Hilton Head Island. It is difficult at
best to reach a scientifically determined limit at or below which the
wetlands will not experience adverse effects. A preliminary draft EES
addressing this problem suggests three alternatives for disposal of
treated effluent, two being land application and the third being
discharge into Calibogue Sound. However, this study is not addressed
to the island-wide problem but to the needs of the Sea Pines PSD only.
The inevitable increasing demands for discharge from other sections of
the island could lead to tremendous water quality problems which will
leave their effects on living marine resources.
The most serious threat to tidal wetlands from present and pending
development has been identified as that of water quality degradation
due to storm water runoff (i.e., storm water which cannot seep
naturally into the ground during rainfall due to the land surface being
covered by buildings, roads, highways, parking lots and other
impermeable surfaces). This runoff picics up many types of bacteria,
chemicals, heavy metals and other toxic materials which are then
carried by the water into the tidal creeks and estuaries. With each
new development the amount of storm water runoff increases and
exacerbates the problem of water quality degradation in the surface
waters around the island. (See Water Quality for further discussion.)
B. Existing Policies, Rules, Regulations, and "State of the Arts"
bindings:
General
Coastal Management Program (111-14,15) These "Guidelines for
Evaluation or all Projects" should be used, without exception, in each
permit application decision. They are most valuable in helping
decision-makers view projects from a broad and comprehensive
perspective.
Discharge of Treated Effluent
Coastal Management Program (III-37, 1 e) Discharge of water used
to pump out holds of fishing vessels must comply with DHEC and Coast
Guard regulations.
Coastal Management Program (111-41, 1 e) Adeauate sewage disposal
systems must oe proviaea oy new commercial development.
Coastal Management Program (III-46, 1 e) Proper handling of
sewage must be maae m new marinas.
Coastal Management Program (111-61, 1 d) "Sewage treatment
facilities snail oe constructed to limit effluent discharge as much as
possible into areas containing productive shellfish beds. Construction
of facilities shall in no case degrade the existing water quality
classification of the receiving water body and if the current
classification is not the highest achievable, the plans shall show a
consideration for the water body ultimately achieving the highest
classification."
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Coastal Management Pro Tram ( III -61, 1 e) "Outfall locations
should consider water depth, circulation and mixing in order to protect
water quality. Effluent should not be discharged into poorly confined
or poorly flushed estuarine areas."
r\ia«rfai Management Plan (111-71, 4) Extension of public services
(e.g., sewer cacihtiesj co barrier islands should only be proposed in
a comprehensive approach considering natural "carrying capacity" of che
island.
Rule 30-12 CE") (4) (hi p. 34 Marina proposals shall include
facilities cor cne proper nanaiang of sewage.
vui? fLl (I) Cd) o. 4* To extent feasible, quantity and
quality ot any waters discharged from drainage canals or ditches shall
not extensively alter wetlands or the quality of coastal waters.
Mon-point Source Pollutants
Management Plan (111-17, 1 d) Drainage plans and
construction measures tor Residential development shall be designed co
control erosion, sedimentation, and water quality degradation on
adjacent water and wetlands. ^Techniques to prevent direct storm water
discharge are suggested.)
Coastal Management Plan CIIX-22, I d) "Care should be taken in
design of roads co minimi redirect drainage of roadway runorf into
adjacent water bodies."
Management Plan CIII-22, 1 f) In construction of private
roadways tor private access permeable surfaces should be used rather
than pavement.
Coastal Management Plan (111-27, 1 b) Proposed parking facilities
most demonstrate compliance with water quality standards concerning
drainage and discharge of storm water runoff.
Vfatia^ment Plan CIII-37, 1 a) Drainage from any proposed
seafood processing operations must meet applicable water quality
standards.
*m„,«,ent Plan CIII-43, 1 e ii) Park plans must
incorporate^ximum use or peraeable surfaces where appropriate.
i Plan UII-
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Water Access Facilities
(marinas, boat ramps, accxs"and piers)
Coastal Management Plan (III-4-6, 1) (Marinas)
"a) To tne extent reasiole carinas shall locate only in areas that
will have the least adverse impact on salt, brackish or freshwater
wetlands and water quality.
b) To the extent feasible marinas shall be located in areas
where maximum physical advantage exists and where the least initial and
maintenance dredging will be required.
c) Marinas should avoid or minimise the disruption o£ currents.
Dead-end or deep canals without adequate circulation or tidal flushing
will not be permitted unless it can be determined that water quality
will not be adversely affected.
d) Marina designs should minimize the need for excavation and filling
of shoreline areas.
e) Provision of facilities for the proper handling of petroleum
products, sewage, litter, waste and other refuse oust be made in new
marinas, with regard to South Carolina Department of Health and
Environmental Control (OHEC) specifications.
f) In review and certification of marina permit applications outside
the critical areas, the Coucil will consider th extent of public demand
for the facilities, as demonstrated by the applicant."
Rule 30-12 (E) p. 32-53 (Marinas)
"(2) Commercial docks are also considered a marina type facility. The
standards that apply to marinas will also be used as criteria in the
evaluation of permit applications for commercial docks.
(3) All marinas affect aquatic habitats to some degree, but adverse
effects can be minimized by utilizing proper location and design
features. Application 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.
(4) In addition to standards for bulkheads and seawalls, docks and
piers, dredging and filling, and navigation channels and access canals,
the following standards are applicable:
a) Marinas should be located in areas that will have minimal
adverse impact on wetlands, water quality, wildlife and marine
resources, or other critical habitats;
b) Wiere marina construction would affect shellfish areas, the
Council must consider the rights of the lessee, if applicable, and
the public, and any possible detrimental impacts on "shellfish
resources;
c) Marinas should be located in areas where maximum physical
advantages exist and where the least initial and maintenance
dredging will be required;
d) Marinas max, avoid or minimize the disruption of currents.
Dead-end or deep canals without adequate circulation or
tidal flushing '-rill not be permitted unless it can be demonstrated
that water qua1 icy will not be adversely affected;
e) Marina design must minimize the need for the excavation and
filling of shoreline areas;
f) Open dockage extending to deep water is usually preferable to
excavation for boat basins, and it must be considered as an
alternative to dredging and bulkheading for marinas;
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g) 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.
Where feasible, boat maintenance areas oust be designed so that
all bottom scraping and painting be accomplished over dry land allowing
for proper contra 1 and deposition of residues, spills and storm water
runoff;
i) Dry storage type marinas are preferred, wherever feasible;
j) Applications for construction of marina and commercial dock
facilities will be considered by the Council only after adequate
demonstration by the applicant of demand for the facilities;
k) Applications for marinas must include maintenance dredging
schedules and dredged material disposal sites when applicable,"
Coastal Management Plan (111-48, 1) (Boat Ramps)
1) in the coastal zone usuncil review and certification of
applications for boat ramps will be based on the following policies:
a) Filling of productive salt, brackish, or freshwater wetlands
for boat ramp construction is prohibited unless no feasible
alternatives'exist in adjacent non-wetland areas. In addition,
the aneunt of fill required must be minimized.
b) The following privities are considered when justifying boat
ramp location in sensitive areas:
i) public use - open to all citizens,
ii) restricted use - open only to citizens of a particular
area or organization,
iii) private use.
c) Boat rase locations requiring dredging of productive salt,
brackish or freshwater wetlands to provide channel access to
deep-water will be discouraged.
d) Boat ramps must be constructed of environmentally acceptable
materials.
Rule 30-12 (B) pp. 29-30 (Boat Ramps)
1) aoat 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
•
2) Specific standards which shall apply are as follows:
a) Filling 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 must be limited
to that which is reasonable for the intended use;
c) Justification for'boat ramp construction in environmentally
sensitive areas shall be considered using the following
orioricies:
i) public use - open to-all citizens;
ii) restricted use - open to citizens of a particular area
or organization only;
iii) orivate use - use for one citizen or family;
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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;
e) 3oat ramp location requiring dredging or filling of wetlands
to orovide deepwater 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 exisitng, abandoned
causeways, provided that these sites comply with other applicable
regulations.
Rule 30-12 (A) pp. 23-29 (Docks and Piers)
g) Dry storage in uplands will be encouraged in preference to
moorage in crowded areas;
h) Developers of- subdivisions, motels, and multiple family
dwellings will be encouraged to develop joint-use moorage
facilities while their plans are in the development stage;
j) Where docks and piers are to be constructed over tidelands
utilised for shellfish culture or other atari culture activity, the
Council will consider the rights of the lessee and the public
prior to approval or denial.
Dredging, Filling and Sooil Disposal
Coastal Management Plan CIII-S5, 1) (Dredging)
TrZ] To the extent ceasible dredging should be performed only
during closed shellfishing season if proposed in a productive
shellfish area.
b) Suspended sediments must be kept to a minimum. The use of
structures such as weirs and silt curtains to minimize water
quality degradation is encouraged. Where highly toxic sediments
are encountered, dredging will be prohibited unless the activity
is consistent with other dredging policies, as well as those for
manufacturing or other industrial activities.
c) Dredging should not reduce water circulation, water currents,
mixing, flushing or salinity in the immediate area.
d) Dredging for establishment of new canals which involves
permanent alteration of valuable wetland habitats will be
prohibited unless no feasible alternative exists or an
overwhelming public interest can be demonstrated. Establishment
of canals for purposes of creating waterfront lots from inland
property, especially where dead-end canals would result, will be
prohibited unless it can be demonstrated that there will be no
significant environmental impacts."
Rule 50-12 (G) p. 37-38 (Dredging and Filling)
**3" tne 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-l2(C), or boat ramps, see R.30-12(3).
All other dredge and fill activities not in the public interest
will be discouraged;
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b) Dredging and filling in wetland areas shall be undertaken only
if the proposed 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 sunns or others*
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 to adjacent areas
during construction by preventing the dispersal of silt material-
f) Dredged materials shall be deposited and contained in such a
manner so as to prevent dispersal into adjacent wetland'areas*
g) Applications for dredging in submerged and wetland areas for
purposes other than access, navigation, mining, or drainaae shall
be denied, unless an overriding public interest can be
demonstrated. Dredaing permits for mining will be issued only as
specified in (2) (hj below. Drainage permits must be consistent
with the provisions in R.jO-12(U;
i) Wetlands shall not be utilized as depositories for waste
materials except as discussed in R.30-12(1);
jj In all cases, dredging activities shall not be approved until
satisfactory disposal sites have been acquired."
Coastal Management Plan
Urilling)
. . Coastal Management Plan £1X1-16, 1 b) Residential development
which wouia require ruling of wetlands will be prohibited, unless nc
teasible alternatives exist or an overriding public interest can be
demonstrated, and any substantial environmental damage can be
minimized.
Coastal Management Plan (III-22, l a) Where wetlands cannot be
avoictec, orxaging ratner cnan filling will be required wherever
feasible.
Coastal Management Plan
upon Disposal J
Coastal Management Plan (111-57, 1) (Dredged Material Disposal 1
"a} ro ene maximum extent teasible, dredged material aust no- )*»
placed on high value .natural habitats such as salt, brackish or
freshwater wetlands; sucmerged vegetaion; oyster reefs or tidal
guts. Where upland disposal is not possible, areas of relativ-?v
low productivity should be utilized, or ocean disposal should be
employed.
b)' Ob land dredge material disposal sites must be stabilized and
maintained where necessary to prevent erosion and direct Cat-r
run-off.
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c) Where water disposal is necessary, natural channels must not
be blocked with dredged material and impact on existing water
circulation should be minimized. Depostion in water areas of
higher flushing rate will decrease damage from suspended sediment
and ox/gen depletion.
d) Consideration must be given to the temporal aspects of spoil
deposition such as impacts on spawning seasons, fish migrations,
waterfowl nesting and wintering areas, and mosquito control.
e) The selection of upland dredge disposal sites should include
consideration for minimizing negative impact on valuable
terrestrial wildlife or vegetative habitats."
Rule 30-12 (F)(2)(b) p. 35: The location and design of public and
private transportation projects must avoid the critical areas to
the maximum extent feasible. Where coastal waters and cidelands
cannot be avoided, bridging rather Chan filling of these areas
will be required Co che maximum extant feasible.
R?ile 50-12 (I) pp. 40-41 (Deposicion of Dredged Material)
77rT Upland disposal of dredged material shall always be sought in
pv. Jference Co 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
alcernative if highland alcernacives are not feasible. However,
open and deep water disposal sites should be seriously considered
only after careful consultation with Che Council and other
relevant state and federal agencies;
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 Co possible adverse
impacts of various alternative sites on che puolic health and
welfare as well as on critical fish and wildlife areas;
h) In all cases, dredging activicies shall not be approved until
satisfactory disposal sites have been acquired."
C. Policies
1. The South Carolina Coastal Council will continue to strictly enforce
its existing policies, rules and regulations affecting the critical
areas of Hilton Head Island and their use. The Council will also
review the cumulative impacts of proposed projects more closely.
2. The S. C. Coastal Council discourages the development of marsh
hummocks around Hilton Head Island, as identified in the Hilton Head
Island Marsh Hummock Inventory. The Coastal Council will continue
to strictly enforce policies, rules and regulations governing access
to these areas.
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The S. C. Coastal Council discourages the closure of any productive
shellfish areas around Hilton Head Island, The following
recommendations will be implemented on Hilton Head Island.
A. Applications for marinas and other activities which would
cause the closure of productive shellfish areas are encouragec
to locate those activities in areas presently closed.
B. No project which will cause the closure of shellfish grounds
designated as being the most productive by the Hilton Head
Island Shellfish Inventory should be approved.
C. Applicants for permitted projects which would cause the
closure of shellfish grounds in less significant areas as
identified by the Hilton Head Island Shellfish Inventory shall
be required to submit a mitigation plan for the loss of
resources to the S. C. Coastal Council, the South Carolina
Wildlife and Marine Resources Department and the South
Carolina Department of Health and Environmental Control.
Excavated, basin-type marinas should not be
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CHAPTER FOUR
Freshwater Wetlands
I. The development and building on Hilton Head Island has resulted in a
number of changes to the natural systems present on the island. These
have included the alteration and reshaping of historic drainage
patterns and land forms, the creation of artificial lagoons and
reservoirs, and the indiscriminate dredging and filling of the
Island's freshwater wetlands.
A. ISSUES: These activities have contributed to the elimination of
approximately 33% of all freshwater wetlands on the island,
toreover, an additional 20% have been significantly changed by
developmental activities occurring on their periphery, which have
resulted in an alteration of the natural patterns which initially
created the wetlands.
The consequences of this continuing trend will be:
1. A loss of wildlife habitat diversity. The loss of wildlife habitat
could result in the elimination of many types of animals on the
island. As natural habitat is lost, the diversity of the animal
peculation will decline resulting in the elimination of the natural
wildlife population.
Z. The loss of areas which have historically been the receiving
point for the collection of storm water runoff and flood events.
As more and more of the island is developed, and undeveloped lands
are replaced by impermeable surfaces, the volume and substance of
runoff water increases. Freshwater wetlands typically are
physical depressions or low spots which collect and hold most
runoff. Retained water is gradually absorbed or filtered back
into the ground or surface waters. Until recently these
wetlands have been set aside from development because of the
availability of other land and the increased costs associated
with, dredging and filling them to make the property acceptable
for building. Competition for space on the island has
changed that. Present trends indicate that these wetlands are
being rapidly developed and removed from the system. Runoff
storm water is instead moved through a system of ditches and
drainage pipes as rapidly as possible to its discharge point.
These systems are designed and "sized" to accommodate a specific
storm event. Any storm larger than the designed storm will result
in water coning out of the ditch and flooding the adjacent area
Prior to development the wetlands were the point where these storm
events were absorbed.
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3.
Reduced natural capacity to treat anA Mi*.
storm west, to important function MsSiLfiS'Sf fron
collection of storm water runoff in watianri. ; f
capacity of these areas. Storm wate^ii^J^ ?eat=»nc
as being pure clean rain wat^ gf^1)r t5°u«ht <*
pollutants are usually found in any urban lJ?^er
with rain as a vehicle of movSeST S^STS"!!1??' *5
transported downstream. Pollutants SJ£ LJS and
street litter; seepage and spm^! SSliS M
stagnant water; cachings; fuei and
fertilizers and pesticide from yards and ®piAjase»
drippings - gas, oils, brake ™Sd£ S^fafSd8?^8"?18
contaminants; dirt and debris washing from cnn«r^S-,-^^r
mosquito control chemicals from aerial spraw£?S£S2!«?Kaa:
seepap from improperly functioning seDticianks^^??w.«.
animal droppings, and dead animals. The aoSmiU?rj!^ *?,¦
of these different pollutants in a single^Ti"i™ 411
ditch, pipe, or low area can result inVoflto^SL^L,
to raw untreated domestic sewage. Surveys of sa?Jl j
taw sewage in localities throughout the^ou^tr^
constituent levels, such as conform bacteria JiJZ? ^
chlorides and miscellaneous substances to be ccSSbl^in
each case. The sampling information conducted^2« J rH
208 water quality program on Hilton Head Island^a.?m.2£» ®
shown high levels of pollutants at several of thesa^t?^3*
stations. sampling
The management of storm water runoff requires that »
coordinated approach be used to address the nroblL a „ _v
of different measures must be used if a successful --- numfer
to be implemented. Best Management Practices u«n--rfT??aa 19
involve holding water on site for periods of time with a
gradual release downstream, a reduction in the amount
pavement and impermeable surfaces, maintenance of
open spaces and natural absorption areas, and good
housekeeping to reduce the introduction of pollutant* *».
systems. Because freshwater wetlands perform a cleaning
function in the natural environment, their abiliti«si« h-u
and filter limited amounts of storm water increase the
importance of their preservation. The amount of water whi^n
can be accommodated by each wetland must, of course be
addressed in the engineering and design phases of each or« im~
proposed for construction. project
4. Loss of aquifer recharge areas. It is highly orobabls
some of the freshwater wetlands on Hilton Head Island are
recharge points for the shallow water aquifer and possibly for
the deepwater aquifer as well. A sue survey is required to
identify these points and verify that an aquifer rscharie i«
in fact occuring. The South Carolina tfater Resources
Commission, during the next year, will be making survevs of
JBny of these wetlands to identify where these points are
located. The elimination of aquifer recharge doints can ha,,,
serious consequents for the island. A fai?^:!} re5£r«
the shallow water aquifer can result in a freshwater draw-down
and contamination or the aquifer by salt water intrusion.
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This could affect Che limited number of people who use shallow
wells for drinking water as well as the number of shallow
wells used for irrigation purposes. Contamination of
the deep water aquifer would affect the total population of
Che island.
The freshwater wetlands of the island can be broadly
classified into four categories. These are: forested (with a
closed canopy), forested (with an open canopy), nonforested,
and the open water community.
The forested (closed canopy) category is made up of a number
of tree comuunities generally containing swamp tupelo,' sweet-
gum, red maple, palmetto, and pond cypress trees.
The forested (with an open canopy) group contains a mixture
of trees and plants dominated by pond cypress, pond pine,
palmetto, tallow trees, marsh, saw grass, foxtail and
cattails.
The nonforested category contains freshwater marsh groups.
Prevalent plants found in this category are marsh,
fern marsh, Virginia chain fern, saw grass, and cattails.
Open water freshwater wetland communities are the floating
aquatic community found in standing water dominated by water
lilies and mosquito ferns, and the pickeral weed community.
The most commonly found forested wetland on the island is the
swamp-tupelo community which predominates the deep wetlands
characteristic of the northern end of the island. The
swamp**tupelo, sweet gum, red maple communites although not as
dominant as the swamp-tupelo group occupy more total area than
any other community." These types of wetlands are found in the
broad, linear wetland northwest of Broad Creek. They often
ran for more than half a mile in length.
Fernmarsh and maidencane marshes are the most common of the
freshwater marshes. The greatest total single area is the
Virginia chain fern, mixed marsh (Wooping Crane Conserancy and
others).
Preliminary investigations provide evidence that most of the
remaining wetlands on Hilton Head Island are 404 Wetlands as
defined by the U.S. Corps of Engineers. However, due to land
development, few 404 wetlands larger than 10 acres still exist
on the island. It is left Co the discretion of the District
Engineer of the U.S. Corps of Engineers whether or not co
allow certain alterations co 404 wetlands less Chan 10 acres in
size.
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B- ^in«-P°UCie5' RUl'S' Reg0lati°"S- mi of tf» lrr«"
"Resiaenciai'^eveiopment'mil^would r eaili re° the*?"Hng'o^othe?1
petroneK alteration of sale, brackish or frsshwter wetlands will
,faa1iMe 3lte"tiv« «i« «¦ an ov«^di^U
public interest can be demonstrated." s
Coastal Management Plan (111-22, 1 a,b,f) Transportation
Road ana aignway routes snould be designed to avoid salt
brackish, or freshwater wetlands. Mo substantial chang-s in water
circulation. Private access ways should be designed to avoid
salt, brackish, or freshwater wetlands.
Coastal Management Plan (111-25, 1 a)
Railways snouia oe aesignea to avoid salt, brackish or freshwater
wetlands.
Coastal Management Plan (111-27, 1 a) Parking facilities
The tilling or otner permanent alteration of productive salt
brackish, or freshwater wetlands will be prohibited unless no'
feasible alternative exists, the facility is directly related to a.
water-dependent activity, any substantial environmental impacts
will be minimized, and an overriding public interest can be
demonstrated.
Coastal Management Plan C111-40. 1 a) Commercial Development
Commercial ueveiopment that requires the filling or other
permanent alteration of salt, brackish, or freshwater v«rTw«
will be denied unless no feasible alternatives^sfa£
facility is water-dependant.
Coastal Management Plan C111-73) Wetlands (outside of
critical areas;
"Project proposals which would require fill or other significant
permanent alteration of a productive freshwater marsh will not JL
approved unless no feasible alternative exist or an overridina
public interest can be demonstrated, and any substantial
environmental impact can be minimised."
TTT Other Management Plan Policies (111-31, Forestry, l-b, l-c
111-32, Mining, l-b, l-c; III-34, Manufacturing, l-b, l-c- tttSa
Fish and Seafood Processing,, l-c; 111-38, Aauaculture 1-i-
*** W*' ni-W, Marinas.'l-a-
111-48, Docks $ Piers; III-S3, Impoundments, l-a, l-b' ITT-?? '
Dredging, l-d; 111-57, Dredged Material Disposal, l-a!) '
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C. Policies
1. The staff of the South Carolina Coastal Council, with the assistance
of other state and federal agencies, will complete comprehensive
site visits to those wetlands identified by the Freshwater Wetlands
Inventory for Hilton Head Island. Designation as a 404 Wetland by the
U.S. Armv Corps of Engineers will provide the primary basis for
investigation and designation as valuable natural resource areas.
Those areas designated as being valuable to the natural systems of
Hilton Head Island should be protected from detrimental alteration.
2. Storm water runoff should be directed into natural drainage routes and
freshwater wetlands, but should not exceed the assimilative capacities
of those areas.
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CHAPTER FIVE
Beaches and Dunes
I Many broad areas of the beachfront of Hilton Head Island are experiencing
erosion. The areas most prone to erosion are North Forest Beach, Palmetto
Dunes, the Folly Inlet and the extreme tips of the island.
A ISSUE* With the excretion of the tips of the islands, where erosion is
IKSniht to result from the currents moving in and out of the two
sounds, most of the erosion is taking place on the orotruding "bump".
Itis thought that this burro could be the sand supply source for the
island ana consequently could account for the increased erosion rate.
Most development which has occurred over the last few years was
set back well beyond the mean high water mark and primary oceanfront
sand dunes. C In some instances houses have been set back beyond the
third line of dunes, and over 22S feet in the case of North Forest
bSS.) More recently, a trend of increased density and maximization
of the oceanfront lots has resulted in building to the edge of the
setback line. These types of projects have typically shown little
reaard for erosion trends and have proceeded to remove existing
sSondary dunes and the maritime forests that provide sand to the beach
system and afford some degree of storm protection.
The erosion protection measures on Hilton Head Island have been
extensive. Presently, most of the area from the Folly Inlet to North
Forest Beach, except for Palmetto Dunes, has to be continuously
renourished and much of it is either protected by a seawall, reyetment,
aroiiTfield, or, in many instances, with both armouring and groin
Ss.ij, A^kHtionallY. two renourishment projects have occurred in the
§5tt« y£5 taoni area- It is not known whether the erosion will
rnnr-ini» The oattem could reverse, and the beachfront could begin
SS tSErww.Forecasting the .rosion rate is vary similar to
forecasting the weather years in advance; too many factors come into
olaywhich can affect the accuracy of these predictions. However, at
i-flic three studies dealing specifically with the beachfront erosion of
Hilwn Head Island have been conducted in the last ten
m„ —j - iot of information has been collected and analyzed.
'It is susoected that the armouring of the shoreline during the last 20
v.ar<. ha-" rBaulted in an increase in size or spread of the area subject
to erosion Permit applications for erosion control structures granted
over the last few years support this belief. Based upon the
information available it was assumed that the erosion rates similar to
those experienced in past years will continue. It is upon this
assumption that these policy issues and recommendations have been
prepared.
Thm «ih«rantial issues involved in the question of protection of
oceanfront.property on the island are:
1 The Council's present policy in approving erosion control
structures is to review each on a case-by-case basis and to
approve each application on its own merits.
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Based upon this existing policy, should the present system of
permitting individual structures be continued or should a
standard design approach - whether it be renourishment,
seawall or revetment - be selected and all future projects
designed to conform to those specifications?
2. The Council '"s present policy is to allow no backfilling in
areas where land has been lost to erosion. Should the Council
allow backfilling behind bulkheads, (in areas where adjoining
bulkheads have been constructed), in order to maintain a
continuous line, which studies have indicated is usually more
effective in reflecting water? If this is allowed should the
use of the area be restricted with a setback line?
3. The Council presently does not enforce any type of setback
requirement behind the primary oceanfront sand dune or point
of highest wave uprush. Development of property which is
presently not subject to erosion has, in many instances,
removed the secondary dunes and maritime forests which
could provide some type of protection in the event' of unusual
weather. Should a setback line and buffer requirement to
protect secondary dunes and maritime forest areas be adopted
by the Council?
4. There is a documented need for increased information on
erosion patterns and the natural systems of the beachfront all
along the coast. A program to take periodic measurements
along the island's coast could be beneficial to the Council
staff, and to scientists, engineers, and developers. The
anticipated program could be conducted with existing staff and
photography. Increased costs could be expected to be minimal.
5. The inlets of tidal creeks are known to be highly unstable
areas. Development pressures will inevitably result in
requests to develop the land around these inlets. The Council
could allow development to occur even though the present
regulations will not be effective in protecting the property
from erosion, sudden flooding, or other events. Should an
increased setback be required?
6. A program to better manage primary and secondary dune systems
remaining after development would be helpful to the
beachfront. It has been recommended chat seme sort of dune
enhancement program be prepared and implemented.
3. Existing Policies, Rules, Regulations, and "State of the Arts"
rintnngs:
Coastal Management Plan Residential Development 2(c), Parking
Facilities *Loj, Manuracturing 2(b), Commercial Development 2(b),
Public Buildings 2(b) . . . The siting of nonwater-depencent structures
on the primary dunes or beaches will be discouraged where other
feasible alternatives exist. Design and construction options which
minimize destruction of the dunes and dune vegetation will be
encouraged.
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„ , vfas-cai wanageawnx r tan ureagea material disposal
2 (a) Upland disposal or oredged material should always be souaht in
preference to disposal in wetlands. ^
,n) SgBl^2|SSSy^ Dune Areas (other than critical areas)
1) flec^p^rnwarpromty to and strong physical and ecological
relationship with beach and primary sand dune critical areas
project proposals in secondary sand dunes oust demonstrate reasoi^bi®
precautions to prevent or limit any direct negative impacts on the
adjacent critical areas.
2) Special attention must be given in new construction activities in
cceanfront areas to prevent or mitigate negative impacts on adjacent
property owners, specifically, increased erosion or loss of protective
dune formations on adjacent lots due to unnecessary destruction 3 or
encroachment onto stable dunes."
Coastal Management Plan Erosion Control Policies (IV-57)
"1) seawalls, ouiJOieaas ana revetments will be considered only as oar-
of a comprehensive erosion control program to insure that these
structures do not cause adverse effects to adjoining propertyowners or
appreciably accelerate erosion in the general beach area*.
23. ... structures must not interfere with existing or planned public
access. . .
3) . . . structures shall not impede public use of beaches below th»
mean high water line. . . w
5) Applications for construction of a seawall in the beach or dim*
critical areas for the purpose of filling behind these jtru^SrefL
create land for private development shall be denied unless the
applicant can clearly demonstrate to the Council that no feasible
alternatives exist ...
6) Except under special circumstances, such as critically eroding
shorelines chat have a direct measureable effect on the economic wall
being of an applicant or are a threat to the public safety, the Council
will promote the use of natural features of tne dune and beach sys-am
rather than artificial protection ..." w
Groins
"*) The positive affect and applicability of a groin system in a
comprehensive shore protection program must be demonstrated."
Artificial Beach Nourishment
1) A thorough stud^/- aust be prepared oerore renourishaent is
attempted.
I) Fill ;naterial should not come from dune fields, adioiniM
beaches or nearshore bars. 8
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Sand Dune Management
"1) Private and public projects to restore and stabilise dunes through
non-structural means are encouraged.
2) To the extent possible, the secondary dunes should be kept in tact
to insure protection of adjoining areas against flooding during storms.
3) Buffer areas should be established, where feasible, to allow for
fnmtal dune growth and movement.
6) Walkover structures are encouraged over all frontal dunes.
However, these walkover structures should not interfere with public
access or extend below the mean high water line.
9) In all cases, the primary fTont-row sand dune, as defined in
R.30-10(B), should not be permanently altered."
Rules and Regulations
Rule 30-13 Specific Project Standards for Beaches and Dunes.
"51 The Council will promote the use of natural features of the beach
and dune system rather than artificial protection,
c) The Council will consider the extent to which the project is
consistent with a comprehensive shore protection program for that
particular stretch of beach,
d) Erosion control structures must not interfere with existing or
planned public access unless other adequate access can be provided,
f) All erosion control projects 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 to the beach . . .
g) Erosion control strucures should not normally be approved except
when erosion imminently threatens permanent improvements, including but
not limited to buildings, paved parking lots, swimming pools, etc.,
which existed on the subject property 90 days after adoption of this
regulation; or, in the case of protecting property adjacent to existing
erosion control structures; or, in the case of structures specifically
called for in an approved erosion control plan."
2) Specific standards for seawalls, bulkheads and revetments.
3) Standards for groins and jetties.
¦t) Requirements for artificial beach nourishment.
Sand Dune Management
1. Requi rsnents for walkways over dunes.
2. Projects to restore or build new dunes.
Ncnwatar-dependent structures ...
The siting of nonwater dependent structures on or over the primary
sand dunes and beaches will be prohibited where other feasible
alternaties exist.
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C. Policies
1. The S. C. Coastal Council will coordinate with development interests
to establish a beach monitoring program for the purpose of
understanding erosion rates and trends on Hilton Head Island.
2. The South Carolina Coastal Council shall emphasize the use of
non-structural solutions to erosion on Hilton Head Island.
3. Erosion control structures should not normally be approved except when
erosion imminently threatens permanent improvements including but not
limited to buildings, paved parking lots, etc.
4. Developers are urged to assess the erosional history of project areas
and to setback their development beyond the jurisdiction of the
Coastal Council where appropriate.
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CHAPTER SIX
Public Access
I. Public Access to the Coastal Resources on Hilton Head Island.
A. ISSUE: The natural resources of Hilton Head Island provide a variety of
recreational activities for the entire public- The more obvious include
swimming, fishing, shellfish harvesting, boating, hiking, and observation
of wildlife.
Several issues have developed in recent years concerning the
appropriate use of these resource areas. Predicted urbanization will only
compound these pro'oIons.
First, while there is an abundance of recreational areas,
access to these areas is usually controlled by private ownership," thus
limiting the use of primary areas to a select public. This is a
particular problem for access to beach areas. Currently there are only
two public beach access points, with approximately two hundred parking
spaces, on Hilton Head Island. It poses a significant problem ffor the
existing population. Second, like beach access, private ownership and a
lack of funds has limited public access opportunities to boat landings.
With the growing trend toward the small tTailerable boat, the.single
public landing on Hilton Head Island will hot meet the public's demand in
future years. In fact, facilities that allow a user fee will likely
became totally private in order to accommodate membership demand. Third,
the construction and location of marinas are already indicating an adverse
impact on many inland fishing drops on Hilton Head Island. This trend will
likely continue should a prediction of ten additional marinas prove
accurate. Fourth, and most important, is the rapid growth factor. Simply,
there is a much greater current demand for access to recreational areas'
than supply. As the interior portion of the island, which possess no
natural access to water courses, develops a tremendous burden will be
placed upon existing supply. Development interests should note that even
the more affluent island residents will find themselves disenfranchised
of the privilege to utilize public recreational resources.
3. Existing Policies. Rules, Regulations, and "State of the Arts" Findings:
Coastal Management Plan CIII-14, Guidelines for Evaluation) 13)
"To protect and, where possible, to restore or enhance the resources of the
State's coastal :cne for this and succeeding generations."
Coastal Management Plan (III-14, 7) "The possible long-range,
cumulative efzects or che project, when reviewed in the context of other
possible development and the general character of the area."
Coastal Management Plan (III-14, 9ii) "Public recreational lands -
conversion or cnese lanas co other uses without adequate replacement or
compensation, interruption of existing public access, or degradation of
environmental quality in these areas,"
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(V««ra1 Management Plan (III-17, 3 B) Developers axe encouraged to
incorporate cannon use recreational areas in proposals for large-scale
residential developments.
Crtjurai Management Plan (IV-44, t) The Coastal Council fully endorses
and will support, turther,md encourage the protection of and the
expansion o£ public access to shoreline areas in South Carolina.
Management Plan (IY-^4, 8) The provision o£ additional parking
space in upland areas adjacent to beaches should be a priority for
recreational planning by both local and state agencies.
9) Lff-al governments in the coastal zone are urged to incorporate
considerations for provision of public access into their local ordinances
and comprehensive plans, especially j*
influence the 1 oca.ten and design of the new developnent that sight affect
"""lo! Prfviti developers in beach areas are encouraged to include
provision of reasonable public beach areas and access ways in their plans.
12) The Council advocates the provision of joint use docks, boat ramps,
dtc
13) The Council recognises the overriding importance of good water
quality as a recreational resource, and will strive to maintain, and
improve, existing standards.
Policies
1 rh#» Smith Carolina Coastal Council should not approve any project or
ihidi wild £u« the net loss of any existing public beach
access.
2- a as^rassr-
dCTelop a™oordinatS plan'o ^
access to the wetland and beach areas of Hilton Head Island.
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CHAPTER SEVEN
Cultural Resources
I. Because of the potential threat to historic and archeological resources
from continued development, it is extremely important that efforts are made
to identify and preserve these surviving reminders of a rich and colorful
past.
A. ISSUE: Hilton Head Island contains a significant number of both
prehistoric and historic sites. Prehistoric archeological sites
consist chiefly of Indian shell-rings and shell middens or mounds which
date back to prehistoric times. Middens and shell rings offer a
glimpse into the little-known life style and customs of prehistoric
native Americans of the Southeast Atlantic coastal plain. In addition
to this cultural information, these sites may yield biological
information which could help to assess the changing conditions of the
tidelands and evaluate present-day management and conservation
practices.
Historic sites on Hilton Head Island are numerous and range from
the former location of fresh water springs, where sailing vessels
renewed their water supplies, to civil war earthwork fortifications,
ruins of antebellum plantation houses and chapels as well as a slave
cabin and numerous cemeteries. They represent an important part of our
state's as well as our nation's heritage and deserve protection as a
tangible link with and an irreplaceable record of past events and
former ways of life.
As development continues on Hilton Head Island, historic and
archeological sites may be threatened by construction of homes,
commercial establishments, roads, highways, marinas and public
facilities. The island's tangible heritage nay be removed or damaged;
historic and cultural information, as yet undiscovered, may never be
brought to light; and the flavor of the island's history may be lost to
future generations. Because of this potential threat, it is extremely
important that efforts are made to preser/e the surviving reminders of
a rich and colorful past.
3. Existing Policies, Rules, Regulations, and "State of the Arts"
rmcnngs:
The S. C. Coastal Council is mandated by Section 2(B) of the
State's Coastal Zone Management Act (Act 123 of 1977):
(2) To protect and, where possible, to restore or enhance the
resources ct the Scare's coastal tone for this and succeeding
generations;
(5) To encourage and assist state agencies, counties,
municipalities and regional agencies to exercise their responsibilities
and powers in the coastal rone through the development and
implementation of comprehensive programs to achieve wise use of coastal
resources giving full consideration to ecological, cultural and
historic '/alues....
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Thus, the Council, through its direct permitting authority
activities in the critical areas as well as its reviL and
certification of other state agency permits, federal aomw-v n,.-,..r,
project proposals subject to A-9S review and Environment^ l£S5 '
Statements, must include, as part of its review, the orot*cti'arTnf
resources of cultural and historic significance.
As a part of this review the Council relies on the Off if* -u.
State Archeologist, S. C. Institute of Archeology and Anthroro W
the S.C. Department of Archives and History for assessments^? any
impacts on cultural and historic resources. (Created in 1967 th«
S.C. Institute of Archeology and Anthropology <« responsible foT
locating, recording, ana excavating prenistoric and historic
archeological sites and publishing interpretive reports on its
findings. In addition to a number of other duties, the S C
Department of Archives and History is responsible for de"7SIo5ina and
carrying out a plan tor tne preservation of the state's wehlSSr??
historic and cultural sites.) one,
Chapter IV of the State of South Carolina CM«r,i u. m T
Program developed by the Coastal council and approved bv tnesSr*
Legislature and the National Oceanic and Atmospheric Administration it
S. Department of Cannerce, contains a section entitled Ceoarachic
of Particular Concern (GAPC's). One of the three cateaor i rh i „
this section is entitled "Areas of Special Historic, Archeoloidcal or
Cultural Significance" and is composed of sites which have beS nL2
to the National Register of Historic Places** as well as sitea^ naned
determined eligible to be named to the National Register Th»«-
classified as GAPC's receive the protection provided by the Coast!?
Council's direct and indirect permitting and review authorities?
The goals of the South Carolina Coastal Zone Management or^
preservation and development of GAPC's of historic, archeolotri ef i"i.
cultural significance are: «™«uog:tcai or
•To give highest priority to the identified primary
value of a 6APC when considering the preservation *r
development of that area. *
To ensure that management of GAPC's is consistent
other policies of the South Carolina coastli ne
management program" (CMP, p. IV-3)
In its review of proposed activities which will impact areas of
special historic, archeological or cultural significance listad
management program, the Council uses the following priority-use
criteria cor these areas, beginning with the use of highest priority:
" 1) Uses which preserve the historical or cultural
values for which che site was placed on the National
Register; '
2) Educational opportunities for the public regarding
the historical, archeological or cultural signified- of
COP p* " If)® M 51" '» ™* disturb*?" 01
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Upon Council adoption o£ a Special Area Management Plan for Hilton
Head island, sites listed in the plan will be given the same protection
accorded GAPC sites.
**The National Register of Historic Places was created in 1966 with
the passage in that year of the National Historic Preservation Act
(P.L. 89-465). This act authorized the Secretary of the Interior "to
expand and maintain a national register of districts, sites, buildings,
structures and objects significant in American history, architecture,
archeology, and culture " The significance of properties nominated
to the National Register is evaluated in accordance with an established
set of criteria. Benefits of listing in the National Register are:
1) makes private property owners eligible to be considered for
federal grants-in-aid for historic preservation through state programs;
2) provides protection by requiring comment from the Advisory
Council on Historic Preservation on the effect of federally assisted
projects on these resources;
3) makes owners who rehabilitate certified historic properties
eligible for federal tax benefits.
C. Policies
1. Sites, including those listed in the Hilton Head Island Special
Area Management Plan (SAMP), should either be left untouched (except
for investigation carried out or authorized by the S. C. Department of
Archives and History and/or the South Carolina Institute of Archeology
and Anthropology) or preserved and/or restored as a tangible record of
past events and former wavs of life.
2. Should it be determined that any site, including those listed in the
Hilton Head Island SAMP, may be adversely impacted by proposed
development, the S. C. Coastal Council will contact the S. C.
Department of Archives and History and the S. C. Institute of
Archeology and Anthropology for coirments and recommendations.
3. Protection of structures and sites shall include one or more of the
following requirements by the S. C. Coastal Council:
A. An appropriate set back line from the site or structure shall
be maintained behind which development may take place.
B. Appropriate vegetative buffers may be required to shield the
site or structure from adverse impacts of uses incompatible to
its special historic, archeological or cultural significance.
C. A reasonable opportunity for professional investigation of the
site or structure may be required at the request of the S. C.
Department of Archives and History and/or the S. C. Institute
of Archeology and Anthropology.
30
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following policies, while not enforceable, are recommended.)
1. Developers are strongly urged to communicate earty-on with the
South Carolina Coastal Council to discuss plans for development in
order to work out potential problems and avoid unnecessary delays and
expense with regard to the review of their projects.
2. Developers are encouraged to seek the assistance and advice of the
Hilton Head Island Historical Society, the S. C. Department of
Archives and Historv and the S. C. Institute of Archeology and
Anthropology in efforts to preserve historic and archeological sites
found on their properties.
3. Because the above list of historic and archeological sites represents
the best information available at^Tesent and is not a totally
complete and up-to-date listing, it is recommended that a
comprehensive cultural resources survey of the area be conducted by
the appropriate agency or agencies as soon as fundine is availahl*'
31
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APPENDIX A
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-------
APPENDIX B. CUBIT ENGINEERING LTD.
CALIBOGUE SOUND DYE STUDY
-------
EVALUATION OF PROPOSED SEWAGE OUTFALL
ON WATER QUALITY OF CALIBOGUE SOUND
JUNE 1902
submitted to
SEA PINES PUBLIC SERVICE DISTRICT
CUBIT ENGINEERING LIMITED
CLEMSON, SOUTH CAROLINA
-------
TABLE OF CONTENTS
1.0 Executive Summary 1
2.0 Introduction 2
3.0 Field Program 3
3.1 Methodology 3
3.2 Results 6
4.0 Numerical Analysis 7
4.1 Numerical Model 8
4.2 Model Parameters 12
4.3 Model Calibration 13
4.4 Results o-f Outfall Analysis 15
5.0 Conclusions 16
References 18
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1.0. EXECUTIVE SUMMARY
A water quality assessment of the proposed Sea Pines sewage
outfall in Calibogus Sound was conducted to estimate its impact
on the area's receiving waters. The scope of services consisted
of a field measurement survey to collect data for the subsequent
numerical model analysis that was performed.
The field study defined hydraulic parameters of the system.
In addition, Rhodamine-WT dye was injected and monitored for a
flood tide cycle to provide information on mixing and upstream
excursion of a pollutant. Dye did not advance beyond Middle Marsh
Island in Calibogue Sound during the period of the study;
furthermore no appreciable, amounts were found in Broad Creek or
the Cooper River past the mouth of Bull Creek.
Some dye entered Bull Creek but advanced no further
than about 6,000 feet upstream from the Cooper River. The
estuary is well mixed as evidenced from measured
temperature/conductivity depth profiles. As a result injected
dye rapidly dispersed to concentrations ranging from an initial
value of about to final readings of at the end of
flood tide flow.
A version o-f the Dynamic Estuary Model was selected to
numerically simulate the estuarine condition*? the model
reproduced tidal flow in the system and calculated several water
quality parameters in response to the advection, dispersion, and
nixing phenomena of the estuary. The calibrated model was used
to simulate the effects on Calibogue Sound of adding a J^boyr <*9<*
discharge of secondary-treatment wastewater. The model showed
1
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that the discharge located near Braddock Cov* would have no
effect on the water quality of the Sound or its tributaries.
2.0 INTRODUCTION
This report presents the results o-f an assessment :jf
effluent discharge in Calibogue Sound resulting from the proposed
Sea Pines sewage outfall. Approximately three million gallons
per day of secondary treated domestic sewage is being considered
for disposal in Calibogue Sound from the Sea Pines Plantation.
Figure 1 shows the general vicinity of the area and the location
of the proposed outfall. In order to assess the environmental
impact of waste disposal in Calibogue Sound and adjacent areas,
the Sea Pines Public Service District contracted with Cubit
Engineering Limited to investigate the outfall concept in terms
of its effect on water quality of the receiving waters.
The study was conducted primarily via a numerical model
analysis of the Calibogue Sound system to simulate the tidal
hydraulics of the area and the behavior of the effluent within
the Sound and its tributaries if continuously discharged into the
system. A field study was also performed to obtain data for
calibrating the model. Tide stage, current velocity and other
physical data were collected to describe the hydrodynamics of the
Sound. In addition, tracer dye was injected at the outfall site
and monitored through a flood-tide cycle to provide information
on dispersion and excursion characteristics within the system;
this was also done for model verification purposes.
2
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his report describes the -field study and numerical model
is in greater detail in the following two sections. An
retation of the results is given in the last section in
of the impact of the outfall on local water quality.
ELD PROGRAM
ethodology
ata was collected in Calibogue Sound for purposes of
ating a numerical model. This section of the report
aes the field work performed and summarises the recorded
In general, the work consisted of injecting a large dose of
scent dye at the proposed outfall location and monitoring
ate of movement, spread, and extent of excursion in
jue Sound and tributary channels on a flood tide. The
«as conducted during March 16-18, 1982, at a time of Spring
>• dye was monitored using three small boats. Two were
s ^ _ . 10 fluorometers to measure the
with Turner Designs Mod©!
surface. Water was pumped
•ration of dye near the
, via a small bilge pump and
'ously through the instrument
. ,. r,4.ed to tracing the movement of
;sembly. One boat was dedicated to
¦ . „i.hor dispatched to various
ncioal dve cloud while the other was ax p
monitor dye movement into
nd tributaries of the estuary to monitor y
i.— 4 normation for the main boat,
channels and provide backup mormauon
: ., j injection at lQW"water, slack
ird boat performed the dye inJBtfclu
d collected numerous surface water samples in Broad
areas and provided logistical support to th o
t.. In addition, th. third boat w« r..p=n,ibl. for
3
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measuring current velocity in the main channel near the out-fall
site.
Horizontal positioning was achieved on the main boat using a
Motorola Mini-Ranger III electronic distance measurer. A series
of -four transponder stations were erected onshore at known chart
positions (Figure 2). By measuring electronically the distance
between any two stations, the position o-f a boat could be
triangulated to an accuracy of + or - 3 meters. The second and
third boats used navigation markers and landmarks to
visually estimate location.
Fifty pounds of Rhodamine-WT dye was injected with the
assistance of a small pump mounted in the boat. Dye was pumped
in a continuous stream at a rate of 0.25 liters per minute while
the boat traversed the throat of the Sound. Approximately 43
minutes was required to deploy the entire quantity of dye in a
back and forth pattern at the surface of Calibogue Sound near the
proposed outfall site. Dye was injected during low^water
under calm wind conditions. In this manner, the dye remained
relatively concentrated prior to the initial stages of flood
tide.
Drogues were deployed in the dye cloud as a means to monitor
its relative movement up the Sound. Their use was principally
qualitative in nature serving as visual tracers to queue times
and locations of flourmeter measurement and maximum excursion of
the flood tide water mass.
Tidal stillwater elevations were measured at two locations
visually using tide staffs. Continuous measurements were made at
Braddock Cove and the Highway 278 bridge. Figure 2 shows the dye
4
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SUBJECT
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SHEET OF
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injection point and the tide measurement locations.
Measurements of dye concentration and tidal elevation
Mere made throughout the flood tide cycle until high water slack.
Data were recorded to map dye movement and dilution of the
principal dye mass in Calibogue Sound and in the tributary
Channels. Tidal current was measured at approximate Hal,-hour
¦ „ «„,h rtr-Pf y .lectromaqnetlc current meter
intervals using a Warsn
sidecasted from an anchored position.
J,w a Martek instrument was used to
On the following day, a IZL
^3i...ra depth and salinity in the
determine the pro-file of temperature, dp
. The Durpose O-f this task was to
water column of Calibogue Sound. The P
well mixed or exhibited any
determine if the estuary
tion. The individual water .ample.
characteristies of strar
„,ior dve concentration in the
collected during the day were read for
evening using the fluorometer*
'4 the various measurements made
Table I gives a summary o
The locations indicated are given in
during the field survey-
figure 2. ^
Location of Eieia Qsasuc-aants
table U MS Wssas
Location
Measurement ^
Velocity ^^ c2> c3f C4f c3
SalinitY ci, C2, C3, C4, CS
Temperature various
Dye various
Drogues stations for
Location bMt
-------
3.2 ' Results
Results o-f the field study are summarisesd in Figures 3
through 7. Stage and current velocity data are reduced in
Figures 3 and 4. Measured dye concentration and characteristics
o-f the dye cloud shape and movement are given in Figures & and 7.
An indication of the degree of mixing experienced in Calibogue
Sound can be seen in Figure 5 by the almost vertical lines of
temperature and conductivity with depth; this is indicative of a
well mixed estuary as would be expected since there is no
substantial freshwater flow to the Sound.
Dispersion and dilution of the injected dye may be inferred
¦from Figures 6 and 7. Figure 6 shows the profile of the dye
cloud at successive time intervals as it progressed upstream in
Calibogue Sound toward Port Royal Sound. Each pro-file
represents the concentration of dye measured by the main boat
while it was anchored on station. In this manner a relative
measure of dye dispersion was obtained by measuring dye
concentration versus time as the cloud flowed past several
stations. The decrease in peak concentration and the lateral
spreading of the dye may be inferred by comparing the successive
measurements. Figure 7 summarizes peak dye concentrations
measured at each of the four monitoring stations. The
concentrations are presented with reference to the Initial
concentration of Rhodamine dye injected. This figure illustrates
the relative dispersion arTtf-mixing which cumulatively reduces the
concentration of dye as it mixes laterally and vertically with
the ambient waters of Calibogue Sound and the tidal prism.
Virtually no dye was observed in Broad Creek; this
6
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phenomenon probably occurred because of hydrodynamic momentum of
water flow northward in Calibogue Sound which hinders transport
across the relatively shallow entrance to the creek.
Dye entered the Cooper River at Haig Point but did not
continue past t-he mouth of Bull Creek at any appreciable
concentration. Instead, the main slug of tracer entered Bull
Creek but progressed no further than the first major bend in the
creek during this study.
Figure 8 summarizes the maximum excursion of the dye within
the study site as well as intermediate peak concentrations that
were measured.
4.0 NUMERICAL ANALYSIS
The second major component of the study consisted of the
development and calibration of a numerical model of the Calibogue
Sound area. The primary purpose of the model was to provide a
capability for predicting the effects of a potential effluent
discharge from the southern end of Hilton Head into Calibogue
Sound and its tributaries. The numerical analysis of water
quality in the system is based upon two primary processes: a
transportation process and a reaction process. The transport
process is hydrodynamic and includes advection, diffusion and
dispersion as welL as the forcing function of the tides and water
inflows from tributaries and waste sources. The reaction process
includes the sources and sinks of a constituent which affects
water quality in Calibogue Sound and that reaction which the
Constituent may experience including physical, chemical, and
biological processes. The reaction process can consist of
7
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sedimentation and f 1 occul ati on of organics, uptake of oxygen by
bacteria, the oxidation of waste and the decay rate of coliform
bacteri a.
4-1 Numerical Model
Several numerical models are currently available which could
be adapted to this problem. However, it was felt at the outset
that because the Calibogue Sound system is not extremely
wide, a one-dimensional model could be employed. The model
chosen for this study is essentially the Dyn^mi r Model
which was presented by Orlob, et al. (1967), Feigner and Harris
(1970), and Callaway, Byram and Ditsworth (1971. This model does
have some minor modifications from the EPA version. This model
is quite similar to the receiving water part o-f the Storm Uater
Management Model with the exception of the addition of
dispersion. The. Dynamic Estuary Model has been used extensively
in estuarine situations to successfully model the hydrodynamics
and water quality.
The one-dimensional representation of flow in an estuary is
given in the Dynamic Estuary Model as:
3h m JL 9uA
at * ~ B 3 x (1)
3u
+ - kufuf + ef-cos a (2)
— 1- U — - » 3x -d
where: A «« channel area
B =» channel width
d ® channel depth
h - tidal stags
u m water velocity
_ m friction coefficient from wind over the water
surface
f » angle between wind and channel alignment
w * wind velocity.
8
-------
The hydraulic friction coef f i ci ent is:
n2
k j-rp . „
(1.49) R ' U)
where: n » Manning's roughness coef f i ci ent
R = hydraulic radius
No Coriolis effect is included in this representation due to
the dimensions of Calibogue Sound. After suitable changes are
made in the above equations, they can be written in finite
difference form. The solution of this set of equations proceeds
independently of the constitutive transport since the density of
the water is assumed constant throughout the system.
Discretisation of the equations of motion for the finite
difference scheme results in a system of channels and junctions.
explicit integration scheme, employing a two-step Runge-Kutta
3rocedure, is used to solve the equations.
The model simulates the tidal flow throughout the estuary as
:*used by fixed tributary inflows and a repetitious tidal forcing
»ction. The calculations produce at even intervals of A t a time
history of head, flow and velocity throughout the system,
"^se parameters are then used as input to the constitutive
!clUati ons.
The quality parameters that are considered in this study are
'^chemical oxygen demand and temperature. These are modeled according to the
*neral transport equations
-------
where: c = concentration of constituent
E = a dispersion coefficient
E s = summation of sources and sinks of the
consti tuent
A source or sink could consist of a reaction with another
constituent. Consider first the relationship for biochemical
oxygen demand (BOD). The equation describing the distribution of
BOD throughout the system is:
ii+ <5>
at 3x ax* i
where L is BOD and K is the deoxyganation rate coefficient.
Likewise the equation for dissolved oxygen, DO is given bys
i£ + U i£ , E 1^7 - K L f K (C -C) -sb
3t 3x 3xz i 2 s e (6)
in which C is dissolved oxygen, K ^ is the reaeration rate,' C
the saturation level of dissolved oxygen, and S is th«
b
benthic oxygon demand. There are numerous other sources and
sinks that could be included in the equations. Although their in-
clusion would more closely approximate nature, these terms would
only add unnecessary complexity to this presentation without
enhancing the accuracy of the results.
The equation describing the transport of fecal coliform in
the system is given by:
3P . 3P _ 3*P „ „
3? + U
10
-------
in which is the conform concentration and K is the die-
away rate of the organisms. Equations (5), (6), and (7) describe
the transportation o-f L, C, and P in the estuarine system and
the interrelationships that exist among these three parameters.
These equations are not completely general but are adequate to
describe the system within reasonable limits. The assumptions
upon which this formulation is based are that:
1. the properties o-f water do not vary;
2. the longitudinal dispersion coefficient is constant
3. the entire system is pseudo-one-dimensional;
4. E is the same for all constituents; and
5. there are no gradients in the vertical or transverse
horizontal direction.
The dependency of Equations (5) and (6) on temperature is through
, l<2 j and Cg . All three of these terms are temperature-
dependent. The saturation concentration of DO varies as:
C - 14.652 - 0.41022T2* 0.007991T2 - 0.000077774T3..(8)
s
for temperature T , given in °C . The deoxyg en at ion rate
:oefficient, Kj , is -functional ly related to temperature as:
ICj (T) ¦ Kj (20°C) [1.047] (T~20) (9)
he reaeration rate coefficient, «2 , is a function of
^mperature as well as channel and flaw conditions. The
emperature dependency is given bys
K2(T) - K2(20bC) [1.024] CT~20) (10)
11
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SUBJECT
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-------
Values of the equilibrium temperature are merely assumed as
input informati on for this particular estuarine system, since
adequate values of solar radiation, atmospheric radiation, long-
wave back radiation, evaporative heat -flux, and convective heat
flux are unavailable.
An explicit integration technique is used in the model to
solve the constitutive Equations (5), <6) , and (7). To minimize
the numerical errors associated with the convective transport
computation, the quartei—point difference solution technique is
used. This technique effectively minimises the pseudo-dispersion
transport and results in reasonably accurate and stable solutions
for adequate time steps in accord with the Curant conditions.
A schematic description of the Calibogue Sound estuarine-
system is shown in Figure 9. To adequately represent
the Calibogue Sound estuarine system a total of 63 channels and
60 junctions were used. The specific characteristics of the
tidal junction and channel data are given in Appendix A. That
cdata includes channel friction, velocities, and tidal elevations
for the initial conditions of the model. The data also include
the geometry of the con-figuration of the model, that is, the
channel—junction relationships.
*•2 Model Parameters
Operation of the model of Calibogue Sound requires the
dentification of several variables and adjustable parameters
lhat re-flect the mechanics, microbiology and chemistry of the
iystem. The hydrodynamics of the model are based on the tidal
12
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variation at the ocean and at Port Royal Sound, the channel
geometry as presented in Appendix A, flow -from rivers and
outfalls, channel roughness coefficients and exchange
coefficient- A single value ;for the roughness coefficient
(Manning's n) of 0.025 was chosen to be representative throughout
the system. Obviously the value will vary throughout the real
system but based on the amount of available hydraulic data, it
was felt that a constant value throughout the system would be
most prudent. There was no significant external flow or
tributaries coming into the system therefore no additional inflow
was input to the model except for that coming from the proposed
outfall at Sea Pines.
In- the water quality model it is necessary to input the BOO
deoxygenation rate, DO reaera^ion coefficient, exchange
coefficient, equilibrium temperature, dispersion coefficient, and.'
decay coefficient for coliform. Additionally, it was necessary
to begin the model at some point, therefore initial condition*
had to be assumed. The model also requires boundary values for
the quality constituents—temperature, DO, BOD and fecal
coliform—at junction 1, the ocean, and junction 2, Port Royal
Sound. Values for the initial conditions are given in Table A.
Likewise values for the rate kinetics ari^ given in Table II.
Although the model has capabilities to incorporate benthic oxygen
uptake, it was decided not to include that factor at this time.
S Model Calibration
The hydrodynamic model was calibrated using the hydraulic
information that was measured in the field study of 16-18, 1982.
13
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The model was compared with the field measured velocities
and water levels. A comparison of the measured tidal heights at
the Highway 278 bridge and at Braddock Cove are given in Figure
3. The measured tidal data are discussed in detail in the
TABLE II-. Rate Kinetics Used i_n Model
Parameter Value
l/day
Reoxygenation 0.23
BOD Decay 0.23
Coliform Die-away 0.3
previous chapter of this report. A comparison of the velocities
obtained at Braddock Point from the model with the field survey
are shown in Figure 4. It is pointed out that the field result#
represent the highest velocities of the section across Calibogue
Sound and when adjusted to give a representative cross-sectional
average agree well with the model results. It is felt that
these results indicate very good agreement between the
hydrodynamics, the model and the* actual measuerements of the
system. Thus it is felt that the predictions that can be made
with the hydrodynamics of the system are adequate for the
evaluation of the effect o-f the proposed waste water discharge.
An interesting result of the hydrodynamics is that there is a net
flow of approximately 10,000 cfs through Calibogue Sound into
sort Royal Sound. Thus any continuously released substance will
3e transported into Port Royal Sound.
To calibrate the water quality aspects of the model it mas
14
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necessary to simulate the instantaneous dye injection which is
discussed previously in this report. Comparisons of the field
and simulated data show good agreement (e.g. Figure 10).
Un-fortunately there are no data available to calibrate the
dissolved biochemical oxygen demand or coliform. In essence the
model is calibrated for the transport of the material with the
addition of some "acceptable rare kinetics.
4.4 Results o-f Outfall Analysis
To investigate the effects of the proposed wastewater
discharge attention was focussed on BOD, DO and fecal coliform.
It was assumed that the outfall discharged continuously at three
mgd (eight cfs) with the following concentrations
dissolved oxygen = 3 mg/1
BOD * 30 mg/1
coliform * 70 MPN/100 ml
Additionally summer conditions were assumed to prevail with ocean
waters at 26 °C rising to 28 *C inside the Sound and its
tributaries.
Simulations o-f water quality were made without the proposed
discharge for background or base conditions. Next, a simulation
was made including the wastewater discharge with the
characteristics presented above. The results of the two
simulations are nearly identical. There is less than one per
cent change in biochemical oxygen demand and no preceptable
change in dissolved osygen. The results are summarized in Table
III. The dissolved oxygen ranged from 6.0 ppm at the ocean
' boundary to as low as 3.03 ppm in the interior locations
13
-------
c;, |R, IPPT IQ RHFFT QF.
A
4
XT
s
k
—5
>
03
i
u.
h
<
~
w
w
2
S
2
o
P
uj
-7
2
UJ
S2
X
I
UJ
£
<£
A
30 -
%0
PELt>
OBSS ? VATIOM:
i ic?
| 2- 3
-TIME IM HOURS
I
8
I
J
0
CD
WAY IM UAA WE CONCEPT* ATI ONI
TIME OF TRAVE.L
Ik) CAU&OG.OE SOUN t? .
comp&sisoio o~ Mas^est> pisu> P4rA wm4
tSBUUTS OF MU/VlffEiCAC vptsBL, CAUSATION}
CUBIT ¦MOIIMMailvte LIIVIITBD r
-------
IABLE I Hi. Summary of D1.s5gl.ved Oxyggn Dl_str l_but j.on irng/l_>
Location Base Condition With Outfall
Atlantic Ocean
6.0
syg®n in the Sound.
Similarly it was noted that the concentration of fecal
coliform did not change when the discharge was added to the
natural system. This can be readily verified by considering the
nixtura of 8.0 cfs containing 70 MPN/100 ml with a net flow over
1 tidal cycle of 10,000 cfs containing a concentration of 20
1PN/100 ml.
;.o CONCLUSIONS
The field study' together with the mathematical model
imulation have shown the hydrodynamie characteristics of
alibogue Sound and its tributaries. In particular the model
hows for the observed tide that there is a net flow of 10,000
16
-------
;ubic feet per second (averaged over a diurnal tidal cycle)
through Calibogue Sound into Port Royal Sound. Most importantly
bhe study has shown that the discharge o-f three mgd o-f secondary—
wastewater would have no e-ffect on the dissolved oxygen
coli-form a-f Calibogue Sound and its tributaries.
:reated
3r -fecal
17
-------
REFERENCES
Callaway, R. J., K. V. Byram, and G. R. Ditsworth,
"Mathematical Model o-f the Columbia River -from the
Paci-fic Ocean to Bonneville Dam," Paci-fic Northwest
Water Laboratory, Environmental Protection Agency,
Part 1, 156 p. (1969), Part 2, 130 p. (1971).
Feigner, K. D., and H. S. Harris, "Documentation Report
Federal Water Quality Administrati on Dynamic Estuary
Model," 0-f-fice o-f Water Quality, Federal Mater Quality
Administration, 248 p. (1970).
Orlob, 0. T., R. P. Schubinski, and K. D. Feigner,
"Mathematical Modeling of Water Quality in Estuarial
Systems, " Proceedings o-f the National Symposium on
Estuarine Pollution, pp. 646-673 (1967).
18
-------
APPENDIX A
-------
«»•«••••••«»••• •••••««•««««« CHANNEL DATA •»•««*••«•»*#« ««
IAN.
LCHCrtl
HI 01II
AREA
MANN 1NC
NET CLOW
ItYD. HAD I US
1
2950.
J 750.
106203.
0.025
9727.12
28. 3
2
3(100.
2'4i»0.
91819.
0.025
9726.09
30.3
3
2850.
1900.
82100.
0.025
9725.15
13.2
1
2100.
1550.
39103.
0.025
10183.23
25.'l
5
23JMI.
1100.
15381.
0.025
10183.23
32. i|
6
1200.
1600.
12271.
0.025
10183.19
26.1
7
1300.
1850.
52580.
0.025
10182.99
28.1
a
1300.
1550.
50217.
0.025
6117.29
32.1
9
1200.
850.
29239.
0.025
6117.30
31.1
10
1300.
150.
11565.
0.025
6117.27
32.1
11
I2U0.
't50.
>1113.
0.025
6117.2/
31.1
12
1300.
550.
16705.
0.025
6117.20
30.1
11
1200.
650.
21295.
0.025
6117.19
37.1
11
13H0.
650.
21015.
0.025
6117. 16
32.1
15
2700.
750.
17535.
0.025
6117.20
23.1
16
3800.
7oO.
17060.
0.025
6117.09
21.1
17
3100.
900.
21038.
0.025
6117.05
23.1
16
5100.
800.
13095.
0.025
2831. 10
16.1
19
1300.
700.
22650.
0.025
-6116.81
32.1
20
2700.
850.
16165.
0.025
3283.13
19.1
21
3800.
700.
11952.
0.025
-3263.10
21.1
22
1200.
1550.
59512.
0.025
1067.35
38.1
23
2100.
1050.
29828.
0.025
1067.32
28.1
21
3500.
1000.
20105.
0.025
1067.25
20.1
25
3100.
700.
15673.
0.025
1067.19
22.1
26
3300.
500.
10181.
0.025
1067.17
20.1
27
1000.
650.
13892.
0.025
1067.12
21.1
28
2200.
750.
12281.
0.025
1067.08
16.1
29
1500.
650.
18386.
0.025
1067.05
28.3
30
3000.
150.
10952.
0.025
-1067.00
21.3
31
6200.
1900.
55910.
0.025
-159.73
29.1
32
6000.
1900.-
52112.
0.025
-159.90
27.1
33
11359.
517.
6923.
0.025
-161.56
13.1
3*1
8159.
1718.
10217.
0.025
1.17
23.1
35
5022.
1312.
30729.
0.025
-116.58
23.1
36
1230.
1057.
21750.
0.025
117.81
23.1
37
6080.
1057.
22636.
0.025
-117.67
21.1
38
7U0O.
1057.
19167.
0.025
0.71
18.1
39
21911.
1057.
11185.
0.025
0.11
13.1
<10
3000.
1657.
192191.
0.025
10191.19
11.3
Ml
2816.
5950.
257970.
0.025
10193.83
13.1
12
5171.
1269.
99629.
0.025
162.66
23.3
13
3231.
1910.
55119.
0.025
162.13
28.1
11
9000.
617.
11903.
0.025
-161.78
18.1
'•5
7503.
1552.
28591.
0.025
0.75
18.1
16
7632.
1291.
23836.
0.025
0.56
18.1
17
13712.
906.
16680.
0.025
0.18
18.1
IB
6168.
3622.
59120.
0.025
1.23
16.1
19
6080.
t035.
23198.
0.025
0.91
22.1
50
5119.
1O50.
11088.
0.025
0.73
13.1
51
2261.
7111.
180507.
0.025
9728.15
25.1
52
3000.
1657.
192195.
0.025
10187.08
11.3
53
3000.
1657.
192193.
0.025
-10186.85
11.3
51
3000.
1657.
192197.
0.025
-10191.21
11.3
55
2816.
5950.
257976.
0.025
-10193.51
13.1
56
2261.
5950.
176507.
0.025
-9727.56
29.7
57
2950.
3750.
106209.
0.025
-9726.72
28.3
5ft
3000.
2100.
91821.
0.025
-9725.61
38. 3
59
2850.
\9Q0.
82099.
0.025
-9725.13
13.2
«««*•«*«•««»* ««*»«««»«*««•« JUNCTION DATA »*#•*¦•»#»#•»
JUNC.
AT ENDS
JUNC.
HEAD
CHANNELS ENTER 1NC
JUNCTION
51
39
1
3.Ml
52
0
0
0
0
20
55
2
3.10
19
30
0
0
0
3
56
1
3.11
58
3
0
0
0
1
5
1
3.11
59
1
31
0
0
5
6
5
3.1U
(t
5
0
0
0
6
7
6
3 .11
5
6
0
0
0
7
8
7
3.11
6
7
0
0
0
a
9
8
3.11
7
8
22
0
0
9
10
9
3.11
8
9
0
0
0
10
11
10
3.11
9
10
0
0
0
it
12
11
3.13
10
11
0
0
0
12
13
12
3.13
11
12
0
0
0
13
11
13
3.13
12
13
0
0
0
11
15
11
3.13
13
11
0
0
0
15
16
15
3.13
11
15
0
0
0
16
17
16
3.12
15
16
0
0
0
17
18
17
3.11
16
17
0
0
0
18
19
18
3.11
17
18
20
0
0
2
19
19
3.11
18
19
21
0
0
18
21
20
3.11
57
2
0
0
0
19
21
21
3.11
20
21
0
0
0
8
22
22
3.11
22
23
0
0
0
22
23
23
3.11
23
21
0
0
0
23
21
21
3.11
21
25
0
0
0
21
25
25
3.13
25
26
0
0
0
25
26
26
3.12
26
27
0
0
0
26
27
27
3.12
27
28
0
0
0
27
28
28
3.11
28
29
0
0
0
28
29
29
3.11
29
30
0
0
0
2
29
30
3.15
63
0
0
0
0
1
31
31
3.11
31
32
0
0
0
31
32
32
3.11
32
33
31
0
0
32
33
33
J. 15
33
11
0
0
0
32
31
31
3.15
31
35
36
0
0
31
35
35
3.15
35
37
38
0
0
31
36
36
3.15
36
37
0
0
0
35
36
37
3.15
3S
39
0
0
0
35
37
38
3.15
39
0
0
0
0
37
38
39
3.11
1
56
0
0
0
51
19
10
3.11
51
11
0
0
0
10
52
11
3.11
55
12
18
51
0
11
12
12
3.11
12
13
0
0
0
12
13
13
3.11
13
11
15
0
0
13
33
11
3.15
15
16
0
0
0
13
11
15
3.15
16
17
0
0
0
11
15
16
3.15
17
0
0
0
0
15
16
17
3.11
18
19
0
0
0
11
17
18
3.15
60
50
0
0
0
17
57
19
3.11
10
53
0
0
0
58
18
50
3.11
52
53
0
0
0
53
11
51
3.11
10
51
0
0
0
1
50
52
3.11
11
55
0
0
0
50
19
53
3.11
51
56
0
0
0
51
10
51
3.11
1
57
0
0
0
52
11
55
3.11
2
58
0
0
0
53
39
56
3.11
3
59
0
0
0
51
20
57
3.15
19
60
0
0
0
55
3
58
3.15
50
61
0
0
0
56
1
59
3.15
61
62
0
0
0 :
-------
60
60B0.
1035.
23 199.
0.025
-0.83
22.'1
'ifl
57
6)
!>'i 19.
man.
I'KI9U.
0.025
O. 63
13.1
5fl
59
62
5'l 19.
2 nn.
2fl'i01.
0.025
0.57
1 3. '1
59
60
63
5*419.
2111.
20101.
0.025
-0.22
13.1
30
60
-------
DATE: July 1, 1982
subject Hilton Head 201 EIS/W.Q. Assessment
from: Qiief, Facilities Performance Branch
to: Robert Cooper, Project Officer
NEPA Conpliance Section
I have reviewed the subject report and find it an acceptable basis to
reinforce our earlier recarmendaticn that a sound out fail 1 is environmental ly
acceptable. However the effluent assumptions regarding dissolved oxygen and
fecal coliform of 5 mg/1 and 70/100 ml do not appear to have any basis.
SCDHEC should be consulted regarding these. Secondary treatment does not
contain a dissolved oxygen requirement. Also, the flow considered is 3 M3D.
Yet this was changed to 8 cts. The inconsistency should be clarified.
John T. Marlar
EPA Form U20-6 (R*v. 3-76)
-------
APPENDIX C. AUGUST 3, 1982 LETTER AND SEPTEMBER 1, 1982
RESPONSE REGARDING WASTEWATER REUSE
-------
RECEIVED MJ6 - 6 1982
AUG V 1312
^ pr-1
I ' l . };. / l n o J i; L11 i r> c n , Ct i.
t'.M.agex , ll-c Pi net Public: Service.- District
P.O. Box :-i/.p.
Hilton Hoed Inland, Soutl: t'a t'Ol ir.a 2i'i2P
fce: Pi J Lor !ki-u Draft HIE
Di l r l-ji . LI1 icon:
l'PA if rev i i; tl.e proceus of cvsluatj rg ell the ccr>ricnte which
'•ore Ltc<-i.vvcv on the Drc.it CIS to that the finsl f.l t*.>rrativc>
c». looti en con k iande. lr the puLlic hearing held en tlx Draft
1-1P i-r-u i• lcJ.~QL<-c a vei y ii.tf.rer-tir.g altc motive . tPA ir i.lno
i i.tcrf rtxd i r. paxiir.izirg tl-c- reuse.- of wastewater «t veil a;.
Frc-ti et j ng f-hellf it";!"¦ v.atom. '-therefore , re believe that >out
>" Iternative (.'(-rc-rvef; a i-» o I c- thorough cnal'/iir? before out" final
" ('i^icr if i.i.oc .
• '-PA I 1.1, r.evcrnl ec-ncernr regarding vaLtevater mar.ager.cnt en
l'i J ton 1a a*. laiart.. In crd-er to fully con ci tier yet. r
<• 3 tei ],c.t ive, I an r treating thr-t you address: how y oi'r prcpc-ta.\
L f- i>c j vtthete cci cor na. Fi rtt, how and vl.er. does thi .<•
t-11<. i r.iit.i xv r <.povf wastewater dicchargc-e fron hevton Ccr.a 1
v'-ici: ctu^t tie i, eec! for t rhel 1 f i ah lo r veat i ng buffer cer.cV
•'¦ecci.',, v ;.at l.ind of back-up cyatei;. it propoaec eurir.g per iocs
°f high t ainiall or oqui[M< i t failure-? Vhire, why ic it
1 -o cc. cLity to pervice the o.irtir.g eeptic tank ar ear s ince
t'ULc ' l cnal} ai c ir.dicrtet; t> ptic t&nks at c l.ot causing the
nci,-point source pollution problems and very few diocur.ented
iaiav.ift ci tl.t re vu ster.e have bet n r.ctcd. Fcut thf l»ov dec s
tl'ir- a 3 tcri.ative avoid proi..otir»g l.igh der.rity gxcvtli and the
r^tultca t additiona l clo-curcc of chcl lliffh areec tsue to
non-pcir.t cource pclluticnV I'ir.clly, vhy dc ytu believe that a
recycle and reu~e cyi-ttin can be inpltiter.ted in a cert effective
and publicly ficci pta!>le Manner'.
RCocper/i;i,V/0 7-1 ^-82/Uf 0 300 X
cc : _'rKandy Gi nbhc7
Fd banaL
OPU Rei-CIii.g File
PA'c PvOc.cj.ng File
-------
-2-
To properly evaluate this new alternative which you have
proposed we request that you provide us with the following
specific additional information.
1. Your proposal involves the expansion of the treatment
plant to 5.0 mgd. Please list the average monthly
flows which you project for this "ultimate build-out"
capacity.
2. When is the expansion of the treatment plant to 5 mgd
expected to be completed?
3. How does the PSD project to utilize the 1.75 MGD in
increased capacity at the treatment plant (i.e., how
much for existing homes on septic systems, how much
for individual vacant lots in existing developments,
and how much for new developments?)? When does the
PSD plan to initiate the removal of existing septic
systems from service and why?
4. Please list the monthly flows which are currently
being applied to the two golf courses now in use.
Indicate monthly commitments which you have received
from the other courses which will be receiving
effluent.
5. Please list the projected monthly loading rates for
the wetlands discharge area. What assumptions went
into projecting these rates?
6. By month, what acreage of road medians, open space and
lawns will be required to dispose of the remainder of
the treated wastewater? Indicate on a map generally
where you expect these areas to be located. What
percentage of the road medians and open spaces are now
being irrigated?
7. What are the drainage patterns of the proposed
disposal areas? How would your plan avoid direct
runoff of irrigated wastewater reaching surface waters
(e.g., irrigation waters hitting paved surfaces;
direct runoff into storm drainage systems, etc.)?
-------
-3-
8. Generally describe the costs which will be associated
with the installation of this system. Costs should
include distribution to individual lots.
9.
10
How will cross connections be avoided when the lawn
irrigation system is set up?
, anticipated from the potential human
What impacts are anut ?
contact with irrigated wastewater?
11 Describe what plans the PSD has for a back-up system
11. Descnoe wna1 * heavv rain or malfunction,
during periods of neavy to*..
u emu in addition to the current 1.8 mgd is
12' p^d asking to discharge into Lawton Canal? For
I 1? How much additional acreage of shellfish
area lilV havfto^be closed for buffer,
13. How ,?»" OTdTA as
existing norP on_point source problems caused by
increased growth and development?
I would lik.e. t0 n^nka/terfve. ^iVordef^o expedite
developing this new ait Piease submit your responses by
completion of the EI°' * for vour continued cooperation on
September 1, 1982. Thank you toi j
i. i • • .
this project.
Sincerely yours,
/s/ Howard D Z-^llor
Actinp,
Charles R. Jeter
Regional Administrator
°c: Roger Davis
-------
SEA PINES PUBLIC SERVICE DISTRICT
P. O BOX 5 1 48
Hilton head island, s c. 29938
803/785-6224
41 BOW CIRCLE
PALMETTO Bay CENTER
September 1, 1982
Mr. Charles R. Jeter
Regional Administrator
United States Environmental
Protection Agency
345 Courtland Street
Atlanta, GA 3036 5
Re: Hilton Head Draft EIS
Our file 8-07
Dear Charles:
This is in response to your letter of August 3/ 1982 requesting
additional information on our alternative for wastewater reuse.
As stated in our presentation on June 23, 1982 at the public hearing
on the Draft EIS, there are a number of questions we have that will
take additional study and design before all the answers are available.
We are happy to provide what answers we can that should be adequate
for you to have confidence that our planned program will work.
For convenience we have listed the questions with our answers
in the order they appear in the letter. From page 1:
1. How and when does this alternative remove wastewater discharges
from Lawton Canal which cause the need for a shellfish harvesting
buffer zone?
The projected ultimate maximum daily flow to the plant is:
Sea Pines 2,358,082 GPD
Forest Beach 1,741,336 GPD
Total 4,099,418 GPD say 4.1 MGD
The ultimate flow for Sea Pires does not include areas currently
served by septic tanks. If all lots served by septic tanks were
added, the total peak daily flow would increase by 355,510 GPD for
a total of 4.5 MGD. it should be noted that the plant flows fluc-
tuate greatly with the seasons. Metered flows for the period March
-------
Mr. Charles R. Jeter
- 2 -
September 1, 1982
In taking a conservative approach we estimate peak ultimate
flows during March through September to be 4.1 MGD and 3.1 MGD the
remainder of the year.
Experience has shown that individual golf courses use up to
600,000 GPD during the hot summer months, but this cannot be guaranteed
for each day. Again, using conservative estimates, the flows may
be reused as follows:
x. • « „rn-iprts for the golf course irrigation and a portion
Construction projects tor^ h^completed by December, 1982.
of the wetlands ^riga d tQ 60o,000 GPD the first year, 1.0
The wetlands progr mgd fche third year. If this program
MGD the second year ld'achieve a zero discharge within three
goes as planned, we could acnieve
or four years.
2. What kind of backup system is proposed during periods of high
rainfall or equipment failure.
„ . -a nf hiah rainfall discharge to the wetlands and
During periods o continue. Golf course irrigation would
landscape irrigatio tests prove that the wetlands can handle
be cut back or stopp • ^ per acre {^5 MGD for 50 acres)
the planned 30,000 g D}an for an additional 50 acres of wetland
then it would be safe to plan r ^ ^
to also handle up to 1.5 muv iuj.
v, consider spray irrigation on half the
Another approach rate of two inches per week, allowing
600 acre Forest L h careful study and planning, we believe
a disposal of 2.3 MGD. to 2#5 to 3<(J MGD ±n the Porest
it will be possible to discnarge
Most of the land in North Forest Beach and Shipyard Plantation
Most or rne xaj Forest Preserve before Pope Avenue
originally drained developments around the Preserve have diverted
was constructed. Land ae th/preserve. Thus, there has been a
storm drainage aw Y i th natural inflow to the Preserve leaving
considerable reduction in
capacity for additional inri
_ 1 « t-hat equipment failure would hinder the operation
_ ls, UJ f J-riiity given the redundancy when the present
of the treatment fa leted (see Exhibit B). During periods of
plant expansion is d /tertiary)effluent could be discharged
extreme rainfall Since the proposed treatment level i?s 5 mg/1
fo^B^oTcK^nd suspended solids» the,effluent will be higher quality
than storm drainage from the land.
5 Golf Courses
Wetlands & Forest Preserve
Landscaped Irrigation
Total Reuse
Summer
2.0 MGD
1.5 MGD
0.8 MGD
4.3 MGD
Winter
1.0 MGD
1.5 MGD
0.6 MGD
3.1 MGD
Preserve.
-------
Mr. Charles R. Jeter - 3 -
September 1, 1982
3. Why is it necessary to service the existing septic tank
since DHEC's analysis indicates septic tanks are not causino th*
non-point source pollution problems and very few documented failures
of these systems have been noted? xaxxures
We do not believe it is necessary to eliminate all the seDtir
tanks in the service area. However, we have sized the treatmeni-
plant to handle these areas should we need to serve them in the
future. As indicated in the answer to question 1, the seDtie tanir
areas require a treatment capacity of 355,510 GPD. By not
these areas the peak flow to the plant in the summer will not exceed
The District's policy has been not to force sewers on the nror^<-
owners using septic tanks. We do respond to petitions from nroDerS
owners asking for sewer service for subdivisions or to the health
department when they determine an area no longer suitable for seDt'
tanks. in either event the property owners have to pay the caDital"0
costs for extending sewers into the area. This cost usuallv nine
approximately $3,000 per lot. y
4. How does this alternative avoid promoting high density orowth
and the resultant additional closures of shellfish areas due to
non-point source pollution?
The fact is that while the EIS was being prepared, Sea Pines
and Forest Beach were being developed out according to master Dlan
that were adopted in the 1960's., Exhibit E is a master map of theS
Sea Pines District showing the current stage of development We
were unable to get a similar map for the Forest Beach District in
the time allowed for this reply. However, after checking with the
Manager of the Forest Beach District and from our own knowledge
of the District, there are only two or three small uncommitted tract-«
available for development. The sewage collection system in both
districts will be loaded to their limits when the ultimate flow
of 4.1 MGD is reached. Massive changes in the collection systems
would be required to increase flows beyond their present planned
limits. Recent moves in Beaufort County and on Hilton Head to mini-
mize land use densities would also help present "up-zoning" of Dronert-w
now developed. "Percy
5. why do you believe that a recycle and reuse system can be imDle-
rctented in a cost effective and publicly acceptable manner? ~
The pipe system used to transport effluent to the five golf
courses in Sea Pines and Shipyard Plantations pass near projects
requiring high volumes of irrigation water. This pipe system would
£>e modified as needed and extended to provide irrigation water to
iigh use areas. If the pumping from the Ocila is not reduced th#»n
the District will be faced with paying its share of the cost to
3ipe water from off-Island sites. This option will be far more
expensive than expanding an existing reclaimed water system within
-he District.
-------
Mr. Charles R. Jeter
- 4 -
September 1, 1982
Reclaimed water has been used in Sea Pines and Shipyard for
four years, with great public acceptance. A more extensive system
has been in use in St. Petersburg, Florida, for seven years with
complete public acceptance. Reclaimed wastewater has been in use
in California since the early 1900's with complete public acceptance.
An extensive four year regional study on health effects of water
reuse in Whittier, Los Angeles County, California was completed
in July, 1982. (I believe the study was partly funded by the EPA.)
After four years of study, no health effects could be found at all
from the use of reclaimed water. Most, if not all residents of
the Public Service District are aware of the Ocala's declining capacity
and would welcome the opportunity to use reclaimed water in order
to conserve potable water. This was evidenced at the public hearing
by comments made by the Sea Pines Association of Property Owners
and by the Island Commission in support of our plan. We have also
had individuals request to connect to the new system serving the
golf courses.
In response to your questions on pages 2 and 3 the following
information is provided:
1. The average monthly flows expected at ultimate buildout would
be:
Month
Avq Daily Flow
Jan
1.6 MGD
Feb
1.6 MGD
Mar
1.8 MGD
Apr
3.6 MGD
May
3.4 MGD
Jun
4.1 MGD
Month
Avg Daily Flow
Jul
4.0 MGD
Aug
3.3 MGD
Sep
2.7 MGD
Oct
2.1 MGD
Nov
1.7 MGD
Dec
1.6 MGD
These average daily flows do not include wastewater from the septic
tank areas. It should be noted that the District has had to plan
the treatment plant for a peak daily flow assuming a near 100%
occupancy. Such a peak day will occur xn August, but not for each
day of the month. The reason August is not the peak month is because
the occupancy rate on the Island is very low the last week of August
due to school starting. The average daily flows for the winter
months are also projected at less than 50% of the summer flows.
There may be individual days during the holidays that exceed this
average but the occupancy in general during these months is very
low. These projections are made with the assumption that occupancy
rates will remain the same for the future.
2. The major components of the 5.0 MGD treatment plant are currently
under construction and will be completed in December, 1982. The
only components that are not adequate for 5.0 MGD are the sludge
digester, the tertiary filters and the disinfection system. Commitments
to provide service have been limited to 3.25 MGD because of the
inability to dispose of the excess treated effluent. These additional
components would be constructed according to a time schedule established
-------
Mr. Charles R. Jeter
- 5 -
September 1, 1982
by DHEC under the "Consent Order." The timing will be based on
design, permit approval, construction and funding. Some of the
components mav be phased with the demand. Everything should be
completed within three to five years depending on the results- of
the wetlands monitoring program.
3. As discussed in previous answers, the actual increase over the
present commitment of 3.25 MGD is only 850,000 GPD for a total of
4 1 MGD The septic tank areas will use an additional 355,510 GPD
if required. New development needs are approximately 550,000 GPD
and capacity for vacant lots in existing developments is approximately
300,000 GPD.
4. The flow to the existing two golf courses are presented for
July, 1981 through July, 1982.
Total Gal/Month Avg Daily Flow
Month Million Gallons MGD
353 1.139
July .
Aug missing
missing
Sept 20 6 0.665
0ct H'I 0.663
Nov H' 9 0.642
?eC 16 9 0.545
? 14! 6 0.521
Fek 14 1 0.455
Mar 5 X 0.170
APr 0*4 0.271
MaY 9'5 0.317
,51 0.810
July za"L
Sfrr-,, rhe low flows during April - June, 1982 were caused bv con
°n at the treatment Plant. The golf, courses had to use «6n
ter as a back-up that was not metered. Use WeH
Formal agreements have been executed with the Sea Pine«s
:3*ny, owner of the four golf courses in Sea Pines Plantation 101
incSth the Hilton Head Company, owner of the 27 hole golf coL
Pyard for sPraVin9 treated effluent on the respective qolf
t "rfef* Each agreement commits to using treated effluent for •
tai irrigation needs. The Sea Pines Company is obligated fco
3 least 1.075 MGD for disposal on the golf courses or in the iwfe^Ve
jfeserve, and the Hilton Head Company is obligated to accept at
3iSSK 375'000 GPD* These commitments combined with the 1.8 MGD
ischarge to Lawton Canal accounts for the permitted 3.25 MGD plant
Pr°jected monthly loading rates were identified bv Wilhnv
-h^ and Associates in their report dated April, 1981, The inff-! v
J *e y®ars of operation were approved by DHEC using a constant
loading rate for each year. A monitoring program will be
-------
Mr. Charles R. Jeter
- 6 -
September 1, 1982
conducted to determine the effect/ if any, for the three different
loading rates. They are:
The assumptions are based on soils tests, rainfall, evaporation,
and nutrient uptake by plant material. This report was reviewed
and approved by DHEC and by the South Carolina Coastal Council.
6. Time does not allow us to provide acreage of road medians, open
space and lawns available for spray irrigation by your requested
response date. We have, however, completed a study of potable water
use for Sea Pines and the entire Island. Copies of the tables related
to Sea Pines and Forest Beach are attached as Exhibit C. We have
found that landscape irrigation for both Districts accounts for
an average of 668,000 GPD during the winter and 810,000 GPD during
the summer. Single-family houses in Sea Pines use an average of
600 to 800 GPD during nine months of the year with 25% of the customers
using an average of 2,3 78 GPD during the summer. The major portion
of this water is used for landscape irrigation.
Our goal would be to stop using potable water for landscape
irrigation and use, in its place, reclaimed water. We are not
suggesting that rates of application be changed by the existing
water users. Therefore, it may be somewhat meaningless to estimate
the acreage of lawns, etc., to be irrigated. From a preliminary
review we believe that we can reduce the use of potable water from
our groundwater supply by 2 MGD. A system supplying water in normal
quantities, as now experienced, to the landscape irrigation systems
as well as to the golf courses would use all the water the treatment
facility could supply. Such a system would save the District money
in expansion to its water system that would be required unless the
projected demand can be satisfied with reclaimed water.
Indicated on the enclosed map (Exhibit E) are locations of
approximately 130 acres of existing irrigated land in Sea Pines
and South Forest Beach that is adjacent to or close to existing
golf course irrigation distribution mains. At a rate of one inch per
week, this 130 acres would use 504,000 GPD. When adding other areas
to this such as Shipyard, North Forest Beach, Palmetto Bay, Harbour
Town, South Beach and single-family lots with irrigation systems,
we feel that our estimate of 0.8 MGD for summer and 0.6 MGD for
winter as stated at the beginning of this letter is conservative
indeed.
7. The existing irrigation systems for landscaped areas use many
small sprinkler heads. Hilton Head is generally flat sandy land.
The existing and future irrigation systems could be inspected by
the District and heads could be adjusted to prevent runoff. In
general this is not considered to be,a problem.
/
198 3
1984
1985
xL, 600, 000 GPD
'1,000,000 GPD
1,500,000 GPD
18.250 Million Gal/month
30.417 Million Gal/month
45.625 Million Gal/month
-------
w _ - 7 - September 1/ 1982
Mr. Charles R. Jeter '
cost associated with a Sea Pines - Forest
8. We cannot es 11 tem without more time and detailed planning.
Beach reclaimed wt £ those areas along the route of existing
The initial cost to p , . reiatively low; however, we will
reclaimed water tiary filters and disinfection system to
have to include the tertiary
meet DHEC requirements.
nrnnram will have to be established. We
9. A cross-connection p g underground irrigation systems having
would allow connection y ^er areas such as St. Petersburg,
no hose bibs. We Will vise,7ot.ems to incorporate their experience
Florida, that have similar systems t
i vrvrfv am
into our program.
n 1a„0i of treatment and disinfection, we would
10. with the Pr°P°®®f . f om potential human contact with irrigated
expect no adverse imPac? J Daper from the EPA titled "A Water
wastewater. We are enclosi:ng Jgburg, Florida" (Exhibit D). We
Quality Success Story - ft. Flora Mae Wellings, Director of
have retained the services Center of the State Department of
Florida's Epidemiology Res® . our preliminary work. We would
Health to consult with us au y _ on our treatment system if
Propose to consult with Dr. the reCyCie project.
we are given conceptual appr
. on the first page of your letter (item
11. This question was asKe question.
2) . Please refer to our answer xo
vstem is approved, we believe that
12. if the reclaimed water sy allQwed 1#8 MGD discharge to Lawton
we will not exceed the Pre?®" I discharge to zero. If the Forest
Canal and will begin reducing J for the five goif courses during
Preserve is not approved as.*,°h ve to discharge the golf course
extremely wet weather, we wixx ^ have pointed out, the quality
irrigation water to the can • ^an the surface runoff.
°f the discharge would oe better
^ „«« non-point problems. We explained
•*¦3. The plan does not a ^r, h maior portions of Sea Pines and Forest
at the public hearing that the ™*Jan/reCOmmendations for controlling
Beach are developed. All s ve]_0proent.
run off have dealt with n
• +.c are created by special legislation
The Public Service Distr.Assembly with specific responsibilities
of the South Carolina General Ass granted to either District.
stated, linage is not has enacted new development
Beaufort County has this f!}f°^oint pollution problems.
regulations that address the non v
show that increased growth
, A look at the enclosed ^Ph«ltesponse is not possible.
eyond our plans discusse conslderations of our plan and
,r review ana. ^molete your review. As
hon^ appPCXate<5wers are adeqU'ate _ questions we, cannot answer
°Pe that these answers y are ®any
Pointed out several times, -
-------
Mr. Charles R. Jeter
- 8 -
septemoer i, dusz
at this time, but we do feel that the facts presented are adequate
for approval to pursue the plan. Please contact me if we can be
of further assistance.
Very truly yours,
SEA PINES PUBLIC SERVICE DISTRICT
i- fj
R. Arnold Ellison, Jr., P.E.
Manager
RAE/apm
enclosures
cc: Roger Davis
William Foster
-------
ACTUAL W. W.
FLOW AT SEA PINES
-------
GENERAL PROCESS FLOW
i«ni«r
M1MU1
ci«nri(tl
SCHEMATIC
CIA*1NC»«
KlUTtO
fUMK -Wl
MMlCft©* lYSTt*
nfmom Ml
-------
TABLE B-13
HILTON HEAD ISLAND
CURRENT WATER USE FOR SEA PINES PSD
Current
No. Units
Tot. Avg.
Winter
MGD
Tot. Avg.
Spring
MGD
Tot. Avg.
Summer
MGD
Tot. Avg.
Fall
MGD
Annual
Usage
10& Gal
Single-Family Residential
2,391
1.077
1.454
1.915
1.629'
546.75
^ondomi ni um/Mul ti-Family
1,649
0.756
0.320
0.434
0.368
169.02
Sprinklers
118
0.322
0.362
0.576
0.540
162.02
Restaurants & Lounges
26
0.043
0.066
0.0B4
0.059
22.53
Retail Shops
35
0.025
0.031
0.051
0.044
13.59
Offices
34
0.030
0.030
0.053
0.052
14.85
Other Commercial
21
0.009
0.010
0.016
0.017
4.68
Total
4,274
2.262
2.273
3.129
2.709
933.59
-------
TABLE B-14
HILTON HEAD
ISLAND
CURRENT WATER USE FOR
FOREST BEACH PSD
Tot. Avg.
Tot. Avg.
Tot. Avg.
Tot. Avg.
Annual
Current
Winter
Spring
Summer
Fall
Usage
No. Units
MGD
MGD
MGD
MGD
106 Gal
Single-Family Residential
513
0.116
0.182
0.212
0.287
71.73
Condom i n i um/Mult i-Fami1y
3,163
0.519
0.690
0.882
0.693
250.56
Sprinklers
46
0.346
0.352
0.376
0.436
135.90
Restaurants & Lounges
19
0.018
0.024
0.025
0.017
7.55
Retail Shops
35
0.006
0.005
0.007
0.006
2.16
Offices
27
0.015
0.010
0.022
0.021
6.12
Other Commercial*
36
0.138
0.ZT8
0.156
0.157
60.21
Total
3,839
1.158
1.481
1.680
1.617
534.24
^Includes:
Adventure Inn (66 rooms) Hilton
Head Inn (200 rooms)
Holiday Inn (200 rooms) Sea
Crest (90 room
Winter 279 GPD/room
263 GPD/room
220 GPD/room
174 GPD/roo^n
Spring 550 GPD/room
360 GPD/room
321 GPO/room
332 GPD/room
Summer 545 GPD/room
456 GPO/room
361 GPD/room
445 GPD/room
Fall 300 GPD/room
422 GPO/room
222 GPO/room
310 GPD/room
-------
TABLE B-ZZ
HILTON HEAD ISLAND
PROJECTED WATER USAGE FOR TOTAL DEVELOPMENT
AREAS 1, 4 & 5 SEA PINES PSD
Type Customer
Winter
Single-Family Residential
Condominium/Multi-Family
Sprinklers
Restaurants
Retail Shops
Office Buildings
3ther Commercial
Winter Totals
Total
No. Units
4,128
3,492
135
35
50
60
25
Avg Daily
Use/Unit
GPD
450
144
2,730
1,470
363
898
7,925
Total Avg
Daily Usage
MGD
1.858
0.503
0.369
0.198
0.018
0.054
0.011
OTT
Total
Qtr.Usage
105 Gal
167.22
45.27
33.21
17.82
1.62
4.86
0.99
270.99
Spring
Single-Family Residential 4,128
-ondomini um/Multi-Family 3,492
sprinklers "5
Restaurants 35
detail Shops 50
)ffice Buildings 60
)ther Commercial 25
Spring Totals 7,925
608
194
3,064
2,500
617
1,298
2.510
0.677
0.414
0.338
0.031
0.078
0.012
O66
225.90
60.93
37.26
30.38
2.79
7.02
1.08
36373?
Summer
Jingle-Family Residential
londomi n i urn/Mul ti - Fami ly
Sprinklers
Restaurants
Retail Shops
Jffice Buildings
)ther Commercial
Summer Totals
:all
4,128
3,492
135
35
50
60
25
rm
>ingle-Family Residential
4,128
•ondomin i um/Mul ti-Fami ly
3,492
Sprinklers
135
Restaurants
35
letail Shops
50
•ffice Buildings
60
'ther Commercial
25
Fall Totals
7,925
800
263
4,880
2,500
490
1,711
681
223
4,580
2,500
351
1,675
3.302
0.918
0.659
0.338
0.025
0.103
0.019
"OP"
2.811
0.779
0.618
0.338
0.018
0.101
0.021
4.787
297.18
82.62
59.31
30.38
2.25
9.27
1.71
-mm
252.99
70.12
55.62
30.38
1.62
9.09
1.55
42T737
°tal Annual Usage
1 ,540.44
B-39
-------
TABLE B-23
HILTON MEAD ISLAND
PROJECTED WATER USAGE FOR TOTAL DEVELOPMENT
AREAS 2 & 3 FOREST BEACH (FOREST BEACH PSD)
Type Customer
Total
No. Units
Avg Daily
Use/Unit
GRD
Total Avg
Daily Usage
MGD
Total
Qtr Usage
10 Gal
Winter
Single-Family Residential 603
Condominium/Multi-Family 2,958
Sprinklers 30
Restaurants 25
Retail Shops 50
Office Buildings 50
Hotel/Motel Rooms 731
Winter Totals 4,447
Spring
Single-Family Residential 603
Condominium/Multi-Family 2,958
Sprinklers 30
Restaurants 25
Retail Shops 50
Office Buildings 50
Hotel/Motel Rooms 731
Spring Totals 4,447
Summer
Single-Family Residential 603
Condominium/Multi-Family 2,958
Sprinklers 30
Restaurants 25
Retail Shops 50
Office Buildings 50
Hotel/Motel Rooms 731
Summer Totals 4,447
Fall
Single-Family Residential 603
Condominium/Multi-Family 2,958
Sprinklers 30
Restaurants 25
Retail Shops 50
Office Buildings 50
Hotel/Motel Rooms 731
Fall Totals 4,447
Total Annual Usage
197
164
6,652
969
142
543
235
213
218
7,660
1,279
169
528
364
371
279
8,173
1,293
191
820
430
325
219
9,472
909
166
779
317
0.119
0.485
0.200
0.024
0.007
0.027
0.172
1.034
0.128
0.645
0.230
0.032
0.008
0.026
0.266
T73IF
0.224
0.825
0.245
0.032
0.010
0.041
0.314
1.691
0.196
0.648
0.284
0.023
0.008
0.039
0.232
1.430
10.71
43.65
18.00
2.16
0.63
2.43
15.48
93.06
11.52
58.05
20.70
2.88
0.72
2.34
23.94
1205
20.16
74.25
22.05
2.88
0.90
3.69
28.26
152.19
17.64
58.32
25.56
2.07
0.72
3.51
20.88
128.70
508.95
B-40
-------
United Slates
Environmental Protection
Agency
Office of Water
Regulations and Standards (WH-551)
Washington, DC 20460
October, 1980
A Water Quality
Success Story
St. Petersburg, Florida
"Waste treatment management plans and practices
shall provide for the application of the best
practicable waste treatment technology before
any discharge Into receiving waters, Including
reclaiming and recycling of water. .
Section 201(b) - Water Pollution
Control Act Amendments of 1972
"St. Petersburg's attitude toward environmental
matters and toward regulatory agencies is remarkable
and refreshing. With persistence and good humor,
St. Petersburg has pursued a goal of water reuse*
Innovative techniques require careful documentation
and an abundance of patience. We are proud of St.
Petersburg on both counts."
K.J. Starzinger, State of Florida
Department of Environmental Regulation
ftice described by the Christian Science Monitor as "one or
America's ten most liveable cities," the City of St. Petersburg's
[uality of life is unique.
Located on the southern tip of semi-tropical, scenic Pinellas
Jounty on upper Tarapa Bay, St. Petersburg is cooled by the waters
nd breezes of Tampa Bay and the Gulf of Mexico. Nowhere in the
ity are you more than four miles away from open water. And
owhere else have people enjoyed St. Petersburg's Sunshine'Offer
- a free newspaper on days that the sun doesn't shine on the
ity, an offer made good only 259 times since the publisher of the
t. Petersburg Evening-Independent started it in 1910.
I
*V4I8.|T
-------
-2-
People flock to urban areas for many reasons — the promise
of profits in a booming local economy, the lure of high-paying
jobs in a dynamic industrial center — but people came to St.
Petersburg by the thousands to enjoy its waterways, its warm
cLinate, and its recreational and retirement opportunities.
Numbering a little over 100,000 in 1950, the city grew to
nearly a quarter of a million by 1977. Moreover, this city
increase has been matched by Pinellas County's growth. Today it
is Florida's most densely populated county.
This population explosion has had a heavy impact on upper
Tampa Bay's quality of life. And one vital aspect of that quality
is providing an adequate potable (drinkable) water supply.
ST. PETERSBURG IS A WATER SCARCE CITY
Much of Pinellas County's history is the story of a continual
search for potable water.
Florida is blessed with the Floridan Aquifer, a thick .
underground layer of potable water which, unfortunately for St.
Petersburg, becomes salty 500 feet under the city. A much
shallower aquifer is located from ground level to a depth of 150
feet, but its water smells of sulfur and is used only for limited
shallow well irrigation.
St. Petersburg's first public water supply was Mirror Lake in
1889, a water body located in the heart of the city, but
population growth soon outstripped the lake's capacity to supply
enough potable water and city officials looked for other sources.
These early attempts to find potable water, which included
drilling wells, were unsuccessful, except to prove that salt water
Intrusion has impacted Pinellas County's potable water.
St. Petersburg was water scarce In 1'930 when the city
purchased its first wellfield to the north of the city to develop
the Costne-~Odessa wellfield which still supplies the city by
pipeline today. .
As the population grew, so did the demand for potable water*
In 1962, St. Petersburg expanded its wellfield holdings by
acquiring the Lutz wellfield northeast of the city, and Weekl
Watehee Spring^. Today, it obtains potable water from its own
wells and from the wells of the West Coast Regional Water Supply
Authority.
Thanks to the foresight of a long line of city officials, to
ownership of its wellfields and approximately 50 miles of
transmission lines, and to its working agreements with the West
Coast Regional Water Supply Authority, St. Petersburg has an
adequate potable water supply through the year 2000.
-------
-3-
But time passes quickly# If the city decided to rely solely
on these present arrangements, how and where would it get potable
water after that?
TIIE CITY TAKES ACTION
Sack In the early 1960's, St. Petersburg had upgraded its
four waste treatment facilities in its northeast, northwest,
southeast and southwest areas to secondary treatment* While these
secondary facilities provided adequate treatment to their
lischarges into Tampa Bay, neighboring communities continued to
lischarge inadequately treated municipal wastes into the bay's
surface waters.
Aware of EPA reports which concluded that Tampa Bay's
ihoreline was highly polluted, and also aware that the Florida
.egislature was about to pass a strict water quality bill (the
'ilson-Grizzle Act of 197? which mandated advanced waste treatment
f all municipal and industrial discharges into Tarapa Bay), in
971 the St. Petersburg City Council authorized a research and
-------
-4-
engineering study to deterraine the most cost effective water
treatment program to conserve potable water and provide best
protection for the water quality of Tampa Bay and adjacent Boca
Ciega Bay.
Working with the Florida Department of Pollution Control, the
U.S. Geological Survey, and the firm of CH2M-HHI, St.
Petersburg's engineering consultants, the St. Petersburg Public
Utilities Department conducted a pilot study to determine the
feasibility of eliminating the direct discharge of the city's
treated waste effluent into Tampa Bay, and to evaluate the
effectiveness of using treated wastewater for spray irrigation
within an urban setting*
The study concluded that given St. Petersburg's potable water
shortage, spray irrigation using treated wastewater was more
feasible and considerably nore cost effective than advanced waste
treatment followed by discharge into Tampa Bay.
On the basis of these conclusions, St. Petersburg decided to
solve its wastewater disposal problem and its chronic potable
water shortage by using advanced secondary treatment and spray
irrigation of the treated effluent to its green areas to save its
potable water for drinking, bathing, and cooking. Once treated to
safe levels, the effluent would be transported by a distribution
system to spray irrigation sites such as city parks, golf courses,
school playgrounds, fields and lawns. Finally, a standby-
deep-well injection system would be constructed to place treated -
effluent underground during high ground water conditions or
extended periods of rainfall.
Determined to go ahead with its wastewater recycling program,
St. Petersburg gave it the green light by including it in its
capital investment program budget for 1972.
In a series of newspaper articles written to enlist financial
support from its citizens, the city conducted a massive public
education campaign to 'make them aware of its potable water
shortage, the need to recycle treated wastewaters for irrigation
to relieve this shortage, and also make them aware that the
Southwest Florida Water Management District had placed
restrictions on using St. Petersburg's potable water supplies for
irrigation.
On October 1, 1972, Congress passed the Federal Water
Pollution Control Act Amendments of 1972 which overhauled previous
«ater quality legislation and began the most comprehensive program
of wacer pollution control in the nation's history by mandating a
sweeping federal and state effort to clean up America's waterways.
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Shortly after the Act was passed, the St. Petersburg City
Council and representatives of CH2M-HHI approached the EPA's
Regional Office IV in Atlanta, Georgia, and the Florida Deparraent
of Pollution Control — known since 1975 as the Florida Department
of Environmental Regulation — in Tallahassee for implementation
funds for a major water recycling program for treated effluent,
cooplete with effluent distribution, spray irrigation and
underground storage.
The City Council bbtained 75 percent federal implementation
funding for the project. These funds, and the money raised by the
city from the sale of revenue bonds, provided the capital to
expand and upgrade the city's existing waste treatment facilities
to advanced secondary treatment, and to plan, design and construct
pipeline distribution systems, deep-well injection systems, and
spray irrigation facilities.
Since the projected irrigation sites were accessible to the
public, the degree of treatment to be determined at the treatnent
plants was of considerable concern, for the city wanted to avoid
human enterovirus-induced public health hazards from the treated
effluent.
Working with Dr. Flora Mae Wellings, one of the world'*
leading environraental virologists and Director of the Florida
Epidemiology Research Center in Tampa, and with the U.S.
Geological Survey and the Florida Department of Natural Resources,
St. Petersburg provided most of the money for a research effort to
develop best practicable treatment to eliminate human
enteroviruses — polio, Coxsackie, and enteric cytopathic human
origin (ECHO) — all of which produce sickness in human beings
ranging from stomach upsets to polio, meningitis and heart disease
present in treated wastewaters sprayed on land.
ENTEROVIRUS REMOVAL ACTIONS
A test project conducted by Dr. Wellings and her staff showed
:hat human enteroviruses present in secondary wastewaters seeped
:hrough Florida's sandy soil, and that enteroviruses from these
wastewaters were present in ground water at depths of 10 and 20
feet after rainfall.
Working with Dr. Welling's staff, CI^M-Hill's engineers
letermined that the safest approach from the public health
tandpoint was to remove enteroviruses in wastewater during
rcatment before spraying these waters on land surfaces.
Dr. Wellings' staff and CH M-Hill conducted a follow-up study7
o test various types of filter aids and filter materials. Data
rom this study showed rhat alum fed into t>ie wastewater stream
efore it passes through a sand and charcoal multi-media filter
ystem, followed by a 30-jpinute chlorination contact period, was
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the most effective method for removing enteroviruses. The
effluent would then receive further, extended chlorination in
covered effluent storage tanks, and additional chlorination during
transport to the irrigation sites, when necessary.
As a result of these investigations, the alutn-fed multi-media
system — which enhances solids-associated enterovirus removal —*
was adopted for all of St. Petersburg's advanced secondary
treatment plants.
FEDERAL CLEANUP ACTIONS
In a letter written on May 19, 1974, to the EPA Regional
Administrator in Atlanta, the St. Petersburg Audubon Society
urgently requested that EPA construction grants to upgrade and
expand the city's Southwest Wastewater Treatment plant be approved
as soon as possible.
"We urge your prompt approval," the letter began, "of the
grant to the City of St. Petersburg for its Southwest Wastewater
Treatment Plant improvements provided under the Federal 1972 Water
Act.
"Ihis will be the first major plant in the country to
accomplish zero discharge to surface waters, total wastewater
reuse and recycling, and best practicable wastewater treatment.
The plans for this facility are of major importance, both iocally
and nationally, as an example of what can be accomplished. Your
approval of the grant can start our city on the way to the
ultimate goal of your agency and the Congress. Further, and of
great importance, is a ruling of the Southwest Florida Water
Management District prohibiting the use of potable water for green
areas. This, together with increasing salt water intrusion, will
place the reuse of treated wastewater for irrigation as the sole
dependable source for golf-courses, parks, and other critical
areas vital to our quality of life.
"We believe the accomplishment of the city in the research
and planning that has been done merits immediate approval of these
funds."
The EPA responded.
On July 14, 1974, the EPA awarded St. Petersburg $14 million
to expand and upgrade its 9 million-gallon-per-day capacity
Southwest Waste Treatment Plant to provide advanced secondary
treatment for 20 million gallons per day of municipal discharges,
and also to construct an effluent distribution system, deep-well
injection systems, and spray irrigation facilities.
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To spray
irrigation sites
\l
Wastewater in
Wastewater Basin
for backwashing
of filters
Chlorine
Contact
Basin
Multi - media
filters
Flow Schematic, Southwest Wastewater Treatment Plant and Recycling System
(Courtesy, CHZM-HILL, Engineering Consultants)
On line in 1977, the new treatment facility — known am elm
Southwest Wastewater Treatment Plant and Recycling System —
consists of the following:
• An activated sludge advanced secondary treatment plant
which removes 90 percent of the biochemical oxygen
demand (a measure of the organic matter In water which
consumes oxygen during biological processes that break
it down) and suspended solids in its discharges*
Treatment includes grit removal, aeration (using oxygen
to break down organic wastes) and clarification
(reducing the concentration of suspended matter In
water).
• The advanced secondary treatment processes include alum
addition, multi-media filtration of suspended solids,
flash chlorination for enterovirus disinfection, and
covered effluent storage tanks to meet night peak
spraying demands. This system produces water which
meets the present Florida numerical standards for
potable water, except for nutrients which are used for
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urban irrigation. The chlorination and multi-media
filtration system reduces enteroviruses to a
non-detectable level. The effluent has a clarity of
about 2.0 Jackson Units (a measure of turbidity in
water); Florida's clarity requirement for drinking water
is no more than 5.0 Jackson Units.
• An effluent distribution and spray irrigation system
which uses all of the treated effluent except during
periods of heavy rainfall. The spray irrigation system
is compatible with the need for water and nutrients of
the plant life being treated. Thus, nature provides
final treatment to state drinking water standards
through its controlled nutrient consumption, returning
high quality water to the ground water table.
• A 20-million-gallon-per-day capacity deep-well injection
system which places treated plant effluent underground
during periods when total plant production cannot be
used.
The Southwest Wastewater Treatment Plant and Recycling System
is served by a master pumping station located at the storage
tanks. This facility can either pump treated effluent into the
Southwest recycled wastewater distribution system — identified by
brown-painted, yellow-striped hydrants and completely separate
from the potable water distribution systeo which brings water into
St. Petersburg from the north — or to the deep-well injection
systeo as a backup during heavy rainfall. Recycled water system
components located above ground are color-coded and shaped
differently than those of the city's potable water distribution
systeo, ensuring that potable water and recycled water will not be
mixed.
On June 27, 1975, the EPA awarded St. Petersburg $18.8
million to expand and upgrade its 8 million-gallon-per-day
capacity Northeast^ Wastewater Treatment Plant to provide advanced
secondary treatment for 16 million gallons per day of municipal
discharges, and also construct an effluent distribution systeo,
deep-well injection systems, and spray irrigation facilities.
This facility went on line in mid-1980.
Then on September 31, 1978, the EPA awarded St. Petersburg
§33.4 nillion to expand and upgrade its 9 million-gallon-per-day
capacity Northwest Wastewater Treatment Plant to provide advanced
secondary treatment for 20 million gallons per day of municipal
discharges, and also construct a pumping station, force mains, an
effluent distribution system, and spray irrigation facilities.
This plant is expected to be operational in 1982.
Apart from differences in treatment capacity, the Northeast
and Northwest facilities are identical in design to the Southwest
plant.
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Finally, between September 1979 arid March, 1980, the EPA
awarded St. Petersburg $348,220 to design a diversion sewer
system, pumping stations, and structural modifications to its
conventional 19-raillion-gallon-per-day capacity secondary
Southeast Wastewater Treatment Plant, which still discharges into
Tampa Bay. Projected to be constructed and operational by the
nid-1980's, these ancillary facilities will divert 6.6 oillion
gallons per day of this plant's municipal discharges to the
Southwest facility, and 6.2 million gallons per day to the
Northwest facility for treatment and spray irrigation. The
Southeast facility's remaining 6.2 million gallons per day of
treated wastewater will be distributed, as needed, to the
metropolitan spray irrigation system.
RESULTS
According to St. Petersburg Public Utilities Division
Director Vincent D. Patton: "By using recycled water for
irrigation, St. Petersburg has reduced its peak demand upon
potable water sources in areas that are presently being sewered by
as much as AO percent, effectively forestalling the day when more
potable water pumping and transmission facilities will be needed.
"In addition, the cost effectiveness of this unique
wastewater treatment and recycling system is shown by the fact
that capital costs, operating and maintenance costs, and energy
requirements are about half the cost of a conventional advanced
wastewater treatment system. This is because nutrient removal,
the most costly treatment cycle, is completed by nature.
"In December, 1976" Patton says, "the total capital cost of
the Southwest Wastewater Treatment and Recycling System u*s $19
million. We've estimated that an advanced waste treatment system
discharging into Tampa Bay and meeting Wilson—Grizzle Act
requirements for a treated effluent containing no more than 5
milligrams per liter (mg/1) of biochemical oxygen demand, no more
than 5 mg/1 of suspended solids, and no more than 3 and 1 mg/1 of
nitrogen and phosphorus, respectively, would have cost
approximately $40. million.
"Finally," Patton says, "assuming that only half of the
treated wastewater is sold to commercial customers at the going
rate of $1.00 per acre per month, as the rest of the effluent
Ust^lbution system is completed and additional spray sites are
:onn£cted, we expect a very large increase in the amount of
reclaimed water use for this purpose. We intend to have this
system pay for its operating costs."
There are other outstanding, long-tera benefits.
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"Land acquisition," says Patton, "a major capital outlay in
any irrigation program, has been eliminated fron the St.
Petersburg system. Private and public landowners have provided
green spaces at no cost and have agreed to pay the city for using
treated effluent.
"St. Petersburg," Patton concludes, "has limited the use of
potable water for irrigation by confining it to lawn-sprinkling on
small land parcels. Today, treated wastewater distribution
systems are being extended to each of the city's quadrants. In
1980, approximately 1,000 acres are under irrigation, and
thousands more will be irrigated once the new distribution systems
are completed. Finally, ftreated wastewater piped to color-coded
hydrants connected to the distribution system also provides fire
protection for the local citizen."
The Southwest Wastewater Treatment Plant and Recycling System
has the distinction of being the first regional plant of its kind
in the nation to produce an effluent in which human enteroviruses
are not detectable.
"Over the years," Dr. Wellings 6ays, "ny staff has monitored
the wastewater from this facility. We've found that when design
criteria are met, no enteroviruses can be demonstrated in the
chlorinated effluent. Even during start-up periods when
malfunctions usually occur,, and before effluents are discharged
into the distribution lines, enteroviruses are demonstrated very
rarely.
"The probability of contracting an enteroviral infection from
exposure to these effluents is so remote," Dr. Wellings
emphasizes, "that I consider it almost nonexistent. Actually, the
chance of contracting such an infection from friends and relatives
is far more likely. However, be cautious. First of all, I don't
intend to drink the effluent to prove my point, but on the other
hand I wouldn't be concerned! if I stood near the spray field. Any
contact except actually swallowing the effluent — which could
cause stomach upsets — doesh't worry me."
Known for her wit as well as her scientific accomplishments,
Dr. Wellings adds another precaution. "Murphy's Law," she says,
"is still in effect: "If anything can go wrong it will.' There
must be careful and continued supervision of all aspects of this
waste treatment system. If a breakdown does occur, disposal
methods other than spray irrigation must be used immediately.
However, provisions for these emergency alternatives are built
into the St. Petersburg system."
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EPILOCUE
According to Joseph Franzmathes, Director, EPA Region IV
Office of Program Integration and Operations: "St. Petersburg's
accomplishment is most noteworthy. For it is one of the very few
cities to have gone through the full research and implementation
cycle of enterovirus removal to the point that it enlisted the
services of a noted virologist to ensure, once and for all, that
there would be no health hazard to human beings exposed to its
treated waters.
"I am equally enthusiastic about St. Petersburg's emphasis on
water reclamation in a water short area, for it will certainly
have a beneficial, long-range effect on any future water
shortages. There's absolutely no question that in terms of civic
responsibility and innovative sanitary engineering, St. Petersburg
is an extremely progressive community."
In April, 1977, the Southwest plant catapulted St. Petersburg
into the national limelight when the National Society of
Professional Engineers selected the project as one of the ten
outstanding engineering achievements of 1976.
It should be noted that this achievement received equal
recognition with another example of technical virtuosity; the
Viking Mars Landing Spacecraft, one of the other nine recipients
honored that year.
(We wish to thank CH_M-Hill, Engineering Consultants, Clearwater,
Florida, for allowing us to use its article New Water. This
informative publication has provided much of the material used in
:his story.)
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