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Draft Environmental
Impact Statement on the
Proposed Port Fourchon
Development Plan,
La Fourche Parish,
Louisiana
Washington, D.C.
July 1978
U.S. DEPARTMENT OF COMMERCE
National Oceanic and Atmospheric Administration
Office of Coastal Zone Management
UNITED STATES
DEPARTMENT OF COMMERCE
DRAFT ENVIRONMENTAL IMPACT STATEMENT
ON THE PROPOSED
PORT FOURCHON DEVELOPMENT PLAN
LAFOURCHE PARISH, LOUISIANA
Prepared by:
Office of Coastal Zone Management
National Oceanic and Atmospheric
^ Administration
Department of Commerce
i 3300 Whitehaven Street, N.W.
Washington, D.C. 20235
6
Digitized by the Internet Archive
in 2012 with funding from
LYRASIS Members and Sloan Foundation
http://www.archive.org/details/draftenvironmOOnati
TABLE OF CONTENTS
PAGE NO.
TABLE OF CONTENTS ±
LIST OF FIGURES
LIST OF TABLES v±i
OUl I lr\t\T i i ■ i ■ i i i i ■ • i i ■ i ■ ■ ■ ■ i i ■ ■ i i ■ ■ x -
THE PROJECT AND ITS IMPACTS
SECTION 1: GENERAL PROJECT DESCRIPTION 1-1
A. SITE 1-1
B. RELATIONSHIP OF PROPOSED ACTION
TO THE TOTAL PROJECT 1-1
C. OPERATION AND MAINTENANCE 1-8
SECTION 2: PURPOSE OF PROJECT 2-1
A. AREA AND COMMUNITIES AFFECTED 2-1
B. NEED FOR PROJECT 2-1
C. ECONOMIC STATUS 2-1
SECTION 3: PROJECT ALTERNATIVES 3-1
A. NO BUILD ALTERNATIVE 3-1
B. STRUCTURAL ALTERNATIVE 1:
BAYOU LAFOURCHE AND LAFOURCHE-
JUMP WATERWAY 3-3
C. STRUCTURAL ALTERNATIVE 2:
WIDENING OF BAYOU LAFOURCHE 3-9
D. STRUCTURAL ALTERNATIVE 3:
REDUCING THE SCOPE OF THE
PROJECT 3-11
E. NON- STRUCTURAL ALTERNATIVE 1 . . . . 3-13
F. NON- STRUCTURAL ALTERNATIVE 2 . . . . 3-14
SECTION 4: PROJECT DESIGN 4-i
A. ENGINEERING DESIGN 4-1
B. ENVIRONMENTAL PROTECTION FEATURES . . 4-12
SECTION 5: COMPLIANCE WITH STATE AND LOCAL
ENVIRONMENTAL PERMITS AND PROCEDURES 5-x
A. STATE PERMITTING PROCEDURES 5-1
B. LOCAL PERMITTING PROCEDURES 5-4
SECTION 6:
SECTION 7:
SECTION S:
SECTION 9:
SECTION 10:
ENVIRONMENTAL SUMMARY &-i
A. ENVIRONMENTAL PROBLEMS WHICH
CANNOT BE SOLVED 6-1
B. MITIGATION 6-7
SHORT-TERM AND LONG-TERM IMPACTS
OF THE PROJECT ?-i
A. LAND RESOURCES 7-1
B. VEGETATIVE RESOURCES 7-1
C. WILDLIFE RESOURCES 7-2
D. WATER RESOURCES 7-2
E. AQUATIC RESOURCES 7-2
F. AIR IMPACTS 7-2
C. ECONOMIC AND SOCIAL IMPACTS
(PRIMARY AND SECONDARY) 7-3
H. RECREATIONAL FACILITIES 7-3
I. ARCHEOLOGICAL RESOURCES 7-3
J. HUMAN ELEMENT 7-3
IRREVERSIBLE AND IRRETRIEVABLE
COMMITMENT OF RESOURCES 8-1
A. LAND RESOURCES 8-1
B. VEGETATIVE RESOURCES 8-1
C. WILDLIFE RESOURCES 8-1
D. WATER RESOURCES 8-2
E. AQUATIC RESOURCES 8-2
F. RECREATIONAL RESOURCES 8-2
G. ARCHEOLOGICAL RESOURCES 8-2
H. AGRICULTURAL RESOURCES 8-2
I. MINERAL RESOURCES [J ?
J. EXISTING DEVELOPMENTS o-j
K. HUMAN ELEMENT 8-3
L. MISCELLANEOUS 8-3
FEDERAL AND STATE INVOLVEMENT 9-1
A. FEDERAL PROJECTS 9-1
B. STATE PROJECTS 9-3
C. OTHER AGENCIES CONTACTED 9-3
D. COMMENTS RECEIVED 9-4
E. EXISTING AND PROPOSED AREA-WIDE
PLANNING AGENCIES 9-7
F. OTHER SOURCES OF FUNDING CONSIDERED . . 9-8
CONSULTATION AND COORDINATION
WITH OTHERS 10-1
A. AGENCIES 10-1
B. PUBLIC PARTICIPATION 10-4
C. PRIVATE PARTICIPATION 10-4
li
EHVIRDNWOTAL DISCUSSION
P AG E N Q,
SECTION A: LAND USE a-i
A. DEVELOPMENT IMPACT A-l
B. IMPACT ON OTHER COMMUNITY FACILITIES . . . A-6
C. MAP INFORMATION A-8
D. GEOLOGY AND PHYSIOGRAPHY A-9
E. HYDROLOGIC ELEMENTS A-23
F. CLIMATOLOGY A-33
G. FLOODPLAINS A-38
H. WETLANDS A-41
I. WILDLIFE HABITAT A-49
J. FARMLANDS A-64
K. RECREATIONAL ELEMENTS A-65
SECTION B: NOISE IfPACTS b-i
SECTION C: AIR QUALITY c-i
SECTION D: WATER QUALITY d-i
A. STATE WATER QUALITY STANDARDS D-l
B. PRESENT CONDITIONS D-2
C. ENVIRONMENTAL EFFECTS D-6
D. WATER QUALITY CHANGES D-8
SECTION E: WASTE WATER TREATMENT PLANTS e-i
SECTION F:. SOLID WASTE WWBENT f-i
SECTION G: HUMAN POPULATION c-i
A. DESCRIPTION G-l
B. ECONOMY G-4
C. INSTITUTIONS G-17
D. DISRUPTION OF SERVICES G-18
E. RELOCATION G-18
SECTION H: TRANSPORTATION h-i
A. HIGHWAYS H-l
B. RAILROADS H-l
C. WATERWAYS H-l
D. PIPELINES ' H-3
E. AIR TRANSPORTATION H-3
F. IMPACTS H-3
SECTION I: WILD AND SCENIC RIVERS 1-1
in
SECTION J: HISTORIC PRESERVATION j-i
A. NATIONAL REGISTER OF HISTORIC PLACES . . J-l
B. ARCHEOLOGICAL AND HISTORICAL RESOURCES . J-l
C. GENERAL ARCHEOLOGY J-2
D. TYPES OF SITES AND LOCATION J-5
E. STATUS J-8
F. GENERAL HISTORICAL INFORMATION {
G. EVALUATION OF SITES j' 10
REFERENCES r-i
IV
LIST OF FIGURES
FIG.
THE PROJECT AND ITS IMPACTS
1-1
1-2
1-3
1-4
3-1
3-2
4-1
4-4
4-5
4-6
4-7
The Bayou Lafourche transcoastal corridor
The Lafourche corridor located between
Terrebonne and Salvador-Barataria estuarine areas.
Port Fourchon development plan
Jetty improvement in Belle Pass
Bayou Lafourche - Lafourche Jump Waterway
The Bayou Lafourche corridor in relation to its
flanking estuaries
Shell road and bank reshaping under construction at
Port Fourchon
4-2 Typical road cross sections at the Port Fourchon
facility
4-3 Proposed channel and slip facilities at Port
Fourchon
EA6J
Typical bank stabilization along Pass Fourchon
at the Port Fourchon facility
Navigation channel improvements in Belle Pass and
Gulf of Mexico associated with the Port Fourchon
facility
Proposed rip-rap at intersection of Bayou Lafourche
and the flotation canal at the Port Fourchon facility,
Typical sections of proposed rip-rap at intersection
of Bayou Lafourche and the flotation canal
1-2
1-3
1-4
1-6
3-4
3-6
4-4
4-5
4-6
4-7
4-8
4-9
4-10
B W IROfE NT AL DI S CUSSION
A-l Port Fourchon area
A-2 Different environments and vegetation of the study
area
A-2
A- 3
A-3 The Port Fourchon study area in relation to the
remainder of Lafourche Parish A-4
A- 4 Land use map of Lafourche Parish A-5
A-5 The Gulf Coast Geosyncline in the vicinity of Port
Fourchon A-10
A- 6 The deltaic sequence in south Louisiana . . A-13
A- 7 The deltaic sequence in south Louisiana A-14
A-8 Contours showing depth to the top of the Pleistocene
formations , A-15
A-9 Physiography of the study region A-15
A-10 Geologic columns from the Port Fourchon area .... A-18
A-ll Subsidence rates, subsurface faults, and salt domes
in the Port Fourchon area A-19
A-12 Historic and projected shoreline retreat in the
Caminada-Port Fourchon area A-20
A-13 Oil and gas pipelines and petroleum fields in the
Port Fourchon area A-22
A-14 General hydrology of the Port Fourchon area A-24
A-15 Average salinity distribution across south central
Louisiana A-25
A-16 Percentage of rainfall excess, South Central
Louisiana A-35
A-17 Paths of hurricanes in the vicinity of the study
area A-39
A-18 Storm surge from the Hurricane Betsy . A-40
A-19 Impounded area in Port Fourchon A-44
A-20 Schematic diagram illustrating morphological environ-
ments and related vegetation associations A-44
A-21 Spoil fill being prepared for Port Fourchon
development A-45
A-22 Port Fourchon beach A-45
VI
LIST OF TABLES
I&BLE PAGE NO,
THF PROJECT AND ITS IMPACTS
2-1 The average effect of the location of a new establishment
(offshore oil associated) in Port Fourchon 2-2
2-2 The average effect of the location of a new establishment
(oilfield service) in Port Fourchon 2-2
2-3 The average effect of the location of a new establishment
(port related) in Port Fourchon 2-4
2-4 Direct and indirect impact of the Port Fourchon
development 2-5
4-1 Development program for Port Fourchon 4-2
6-1 Adverse effects on archeological sites of the area . . . 6-4
6-2 Degree of importance each archeological site should
receive 6-5
ENVIFWP1TAL DISCUSSION
A-l Geologic column of the study area A-ll
A-2 Physical characteristics of depositional environments , , A-16
A- 3 Oil and gas production in Lafourche Parish compared to
Louisiana (1970) A-21
A- 4 Hydraulic data at selected sites A-30
A- 5 Monthly tide levels in feet along the Central Louisiana
Coast, 1958-59 A-31
A-6 Annual wave climate .summary for Coastal Louisiana .... A-32
A- 7 Monthly precipitation in inches, Southeast Division . . . A-34
A-8 Percentage frequencies of relative humidity observations
at 6 A.M. and 3 P.M., during midseason months A-36
A-9 Frequency in percent of winds from various directions
in the Gulf of Mexico A-37
VII
WLL PAGEUP .
A-10 Plants associated with environments located within the
Port Fourchon complex A-42
A-ll Saline marsh as affected by spoil banks within the
impounded area A-43
A-12 A list of vascular plants present in the study area . . A-47
A-13 Recreation provided in past years and for 1971-1979
Wisner Wildlife Management Area A-51
A-14 List of species of fish common in the study area . . . A-61
A-15 Participation by activity of persons six years and
older, Region 3 A-66
C-l Average percentage frequency of occurrence of wind
speed - July C-2
C-2 Average percentage frequency of occurence of wind
speed - September C-3
C-3 Average percentage frequency of occurrence of wind
speed - October C-4
C-4 Average percentage frequency of occurrence of wind
speed - December C-5
D-l Hydrologic and water qualify data, lower Bayou
Lafourche at Gulf of Mexico D-3
D-2 Hydrologic and water quality data, lower Bayou
Lafourche 5.0 miles, south of Leeville, Louisiana . . . D-4
G-l Population increases 1960-1970, Lafourche Parish and
Louisiana G-l
G-2 Population characteristics of Lafourche Parish compared
to Louisiana (1970) . G-2
G-3 Projected population - Lafourche Parish G-2
G-4 Population Lafourche Parish and Ward 10 G-3
G-5 Percentage distribution of employment by major industry
in Lafourche Parish G-5
G-6 Payroll distribution in Lafourche Parish, Louisiana,
and the United States, January - March, 1972 G-6
G-7 Families at various income levels, Lafourche Parish,
1969 '
viii
IABLE PA CE NO .
G-8 Percent of families with incomes under $3,000 and
$10,000 and over, Lafourche Parish, Louisiana,
and the U.S.A., 1969 G-7
G-9 Selected agricultural statistics for Lafourche
Parish, Louisiana (1974 and 1969) G-8
G-10 Total commercial landings of fish and shellfish in
Louisiana G-9
G-ll Quantity and value of commercial landings at certain
Louisiana fishing ports (1971-1973) G-10
G-12 Volume of shrimp ' landings (Heads-off basis) reported
in Lafourche and Terrebonne Parishes, Louisiana . . . G-ll
G-13 Quantity and value of oyster landings, Lafourche
Parish, Louisiana G-ll
G-14 Total and average wages and employment in fisheries,
canned and cured seafoods, and fish processing and
packaging industries in Lafourche Parish G-12
C-15 OiL and gas production in Lafourche Parisli compared to
Louisiana (1970) C-13
G-16 Petroleum, natural gas, sulphur, natural gas liquid,
(Minerals in order of value), 1973-1974 G-13
G-17 Curde petroleum production and wells completed in
Lafourche Parish, by area G-15
G-18 Manufacturers in the Port Fourchon area (1972) .... G-16
G-ZU Composite health status indicator, Lafourche Parish,
Louisiana, and nation (1971) G-18
G-21 Direct and indirect impact of the Port Fourchon
development U-19
H-l Volume of freight traffic on Bayou Lafourche H-2
H-2 Major commodities shipped on Louisiana segment of Gulf
Intracoastal Water Way in 1969 H-2
J-l Coastal Louisiana culture sequence and chronology . . J-3
J-2 Percentages of decorated sherds for two sites in the
Port Fourchon area J-4
IX
SUMMARY
C x) Draft Environmental Impact Statement
( ) Final Environmental Impact Statement
This document was prepared by the Department of Commerce, National
Oceanic and Atmospheric Administration, Office of Coastal Zone Manage-
ment. For additional information about the proposed action or this docu-
ment, contact:
Office of Coastal Zone Mangement
National Oceanic and Atmospheric Administration
3300 Whitehaven Street N.W.
Washington, D.C. 20235
Telephone: 202/254-8000
1. TYPE OF ACTION
( x) Administrative ( ) Legislative
2. BRIEF DESCRIPTION OF THE ACTION
As part of the coastal zone management activities of the Federal
government, the Secretary of Commerce administers and coordinates a
coastal energy impact program (CEIP) under Section 308 of the Coastal
Zone Management Act as amended (16 U.S.C. 1451 et seq.). The CEIP pro-
vides financial assistance to coastal states and units of local govern-
ments within those states to mitigate the on-shore impacts of coastal
energy activities.
The proposed action is a loan offer for the amount of $6,300,000.00
to the Greater Lafourche Port Commission to fund the fourth phase of a
multiport facility to accommodate the needs of the fishing/seafood in-
dustry, recreation/ tourism industry, the offshore oil industry and the
Louisiana Offshore Oil Port, Inc. (LOOP). Phase 4 consists of:
a) Dredging a channel and slip and fill in Pass Fourchon as well
as relocating and maintaining an entrance channel at Belle Pass;
b) Making stone jetty improvements at Belle Pass ( Bayou Lafourche);
c) Dredging and stabilizing a flotation canal;
d) Making drainage improvements; and
e) Constructing a bulkhead for docking facilities.
xi
New construction and improvements will require dredging a total
of 2.957 million cubic feet of spoil which will result in an aver-
age increase in elevation of 3.84 feet at the spoil sites. Phase
4 is described in more detail in Section 1, pages 6-7.
The port facilities will be wholly owned by the Greater
Lafourche Port Commission, a unit of general purpose government
as defined in the Coastal Zone Management Act, as amended, Section
308(1X3). The system of user charges to provide the primary
source of repayment of the loan over the 30-year life of the faci-
lity is described in the project document files located at the
Office of Coastal Zone Management at the above address.
3. SUMMARY OF ENVIRONMENTAL IMPACTS AND MITIGATION MEASURES
Short term benefits of granting a loan to construct Phase 4 of
the port facilities are an increase in construction-related employ-
ment and an increase in disposable income which will be spent for
housing and services in the communities near the port site.
Combined with the first three phases of the port development,
the long term benefits of this action will affect the economic base
of Grand Isle and local communities north of Golden Meadow in
Lafourche Parish. The commercial marina, docking facility and
warehouses should attract larger shrimp boats and seafood processing
industries for a net increase in employment and tax revenues for the
Parish. The five-ramp launch for sport boats should attract recrea-
tional fishermen who will need services from the local communities.
The bridge providing access to the beach should attract land-based
day users to the area which will benefit the local economy. Phase
4 will result in the creation of 450 acres of land to provide a site
for future industrial and commercial development. If this develop-
ment occurs, the employment and tax base of the Parish would increase
significantly. LOOP, Incorporated, estimated that employment for 250
permanent full time persons would be generated by the offshore oil
port. Property tax generated by the LOOP facility was estimated at
$32,000 to $49,000 annually.
Short term costs will primarily affect water quality and wildlife
habitat. There will be a temporary increase in turbidity and loss of
benthic organisms as a result of dredging and onshore construction.
The degredation of water quality will reduce the food supply for
aquatic species and disrupt breeding and feeding activities of aquatic
species and waterfowl in parts of Bayou Lafourche and Belle Pass. On-
shore construction will disrupt the breeding and feeding activities of
terrestrial species, though the habitat affected has already been
disrupted by previous dredge spoil disposal.
Long term costs of Phase 4 can be grouped into five areas: land
use, flood problems, recreation, terrestrial wildlife habitat, fisher-
ies habitat and special concerns.
Land use changes involve loss of 55 acres of land for construc-
tion of the T-slip and creation of 450 acres of dry land around the
T-slip for the industrial/commercial site. The 450-acre site is
currently a combination of brackish marsh habitat and old spoil
disposal sites. Past spoil disposal has raised the land 6 to 12
inches; project-related dredging will raise the site another 3 feet.
If development does not occur immediately at this disposal site, it
will accommodate spoil from maintenance dredging for 20 years. As
use of the port facilities increases, the rate of beach and shore-
line erosion will increase as a result of wave wash from passing
vessels .
Storm surges and torrential rainfall will generate floods
periodically at the project site. Past floods have attained depths
of 10 feet or more in the project area which will be elevated less
than 10 feet above mean sea level by fill. The proposed site is
within the 100-year floodplain as mapped for the U.S. Department
of Housing and Urban Development in May 1971. The project is not
presently specifically designed to minimize potential harm to the
floodplain, to meet f loodproof ing standards under the National
Flood Insurance Program or to be in compliance with the Flood Dis-
aster Protection Act. However, the facilities are located behind
the beach which serves as a natural buffer to reduce the force
of storm surges.
Changes in recreational uses at the project site will result in
the loss of revenues from current fishing and duck hunting activities
when the 450-acre marsh/spoil site is converted to dry land. Pro-
viding better access to the barrier beaches is anticipated to in-
crease their use. Increased use will result in the loss of beach
vegetation and an increase in the rate of beach erosion. Currently,
the shoreline is retreating at a rate of just over 20 meters a year.
As the land at the 450-acre site is committed to roads, ware-
houses and other industrial/commercial uses, the habitat available
for terrestrial species will be reduced. The conversion of the area
from a migratory waterfowl feeding area to dry land is a more signi-
ficant change in habitat than the loss of marginal habitat on re-
vegetated dredge spoils.
The long term loss in fisheries habitat will result from changes
in the hydrology of the project area. Widening and deepening the
channel at Belle Pass will increase the salinity in Bayou Lafourche
and adjacent marsh/estuarine habitats. Two of the most productive
estuarine areas in the United States are located immediately to the
east and to the west of the project area; they are the Caminada-
Barataria and the Timbalier-Terrebonne estuarine systems, respectively.
Bayou Lafourche is hydrologically connected to both of these systems
and serves as a passageway for the movement of marine organisms into
and out of the estuarine areas at different stages in their life
cycles. Increases in salinity will create a barrier to this movement
of organisms, reducing the productivity of the estuaries. The impact
of saltwater intrusion on the Tinbalier-Terrebonne system could
be mitigated by restricting water exchange through the tidal
streams which connect lower Bayou Lafourche and Timbalier Bay.
Special concerns relate to identified endangered species
and archeological sites affected by the project. The project
will encroach on the feeding areas of the endangered brown pelican,
bald eagle and peregrine falcon near the mouth of Belle Pass. The
brown pelican, Louisiana's state bird, was only reestablished in
the state coastal zone in the 1960's. The project area also is
in the range of three endangered species of sea turtles, but the
use of the project area by these species has not been established.
Project construction will affect six archeological sites, but only
two are significant enough to be eligible for nomination to the
National Register of Historic Places. These two sites will be
protected from being buried under dredge spoil during project con-
struction. However, increased bank erosion, vandalism and main-
tenance dredging will affect all the sites over the long term.
4. ALTERNATIVES CONSIDERED
The no action alternative was rejected because of the economic
benefits which would be lost. Port Fourchon is strategically
located between the LOOP project site and the Lafourche trans-
coastal corridor. In addition, the first three phases of the port
are well underway; failure to fund Phase 4 will not eliminate many
of the impacts of the project.
Structural Alternative 1, the Bayou Lafourche and Lafourche Jump
Waterway, was rejected because of adverse impacts on archeological
sites, saltwater intrusion into a municipal water supply and adverse
effects on estuarine ecosystems which include parts of the Point~au-
Chien Wildlife Management area and the Wisner Wildlife Management area
Structural Alternative 2, Widening of Bayou Lafourche, was re-
jected because of adverse impacts on the human environment, particu-
larly relocation of existing facilities, residences and roads. In
addition, widening the bayou would eliminate most of the land suit-
able for development so that growth would encroach further on wetlands
Structural Alternative 3, Reducing the Scope of the Project, was
rejected because it would foreclose options for responding to future
needs of the offshore mineral extraction industry. In addition,
implementing this alternative might have the effect of overtaxing the
planned facilities at Morgan City in adjacent St. Mary's Parish,
described in the U.S. Army Corps of Engineers' Draft Supplement to
Final Environmental Statement — Atchafalaya River and Bayous Chene,
Boeuf and Black, Louisiana.
Nonstructural Alternative 1, reducing the offshore energy acti-
vities, was rejected because it would not be feasible in view of
present national energy needs.
Nonstructural Alternative 2, Expanding Other Existing Small
Port Facilities in the Region, was rejected because it would result
in increased boat traffic through waterways in environmentally
sensitive areas of the coastal zone and would induce expansion
into wetlands at many sites, rather than concentrating development
and wetland losses at one site.
5. DISTRIBUTION
Comments have been requested from the following Federal, state
and local agencies and other parties:
FEDERAL AGENCIES
Advisory Council on Historic Preservation
Department of Agriculture
Department of Commerce
Department of Defense
Department of the Navy
U.S. Army, Corps of Engineers
U.S. Air Force
Department of Health, Education and Welfare
Department of Housing and Urban Development
Department of the Interior
Department of Justice
Department of Labor
Department of Transportation
Economic Development Administration
Federal Energy Regulatory Commission
General Services Administration
Marine Mammal Commission
National Oceanic and Atmospheric Administration
U.S. Coast Guard
U. S. Department of Energy
NATIONAL INTEREST GROUPS
American Association of Port Authorities
American Bureau of Shipping
American Fisheries Society
American Institute of Merchant Shipping
American Petroleum Institute
American Water Resources Association
American Waterways Operators
Barrier Islands Coalition
Center for Natural Areas
Coastal States Organization
Conservation Foundation
Environmental Law Institute
Gulf South Atlantic Fisheries Development Foundation
Izaak Walton League
League of Women Voters Education Fund
National Association of Dredging Contractors
National Audubon Society
National Fisheries Institute
Natural Resources Defense Council
National Wildlife Federation
Shipbuilders Council of America
Sierra Club
Sport Fishing Institute
STATE /LOCAL AGENCIES
Advisory Board to the Governor's Council on Environmental Quality
Capital Resources, Conservation and Development Project
Central Lafourche Regional Planning Commission
Community Improvement Agency
Crescent Soil and Water Conservation District
Greater Lafourche Port Commission
Jefferson Port Commission
Lafourche Basin Levee District
Louisiana Coastal Commission
Louisiana Department of Conservation
Louisiana Department of Environmental and Development Control
Louisiana Department of Highways
Louisiana Department of Natural Resources
Louisiana Department of Public Works
Louisiana Historical Preservation and Cultural Commission
Louisiana Wildlife and Fisheries Commission
Morgan City Harbor and Terminal District
President's Water Pollution Control Board
Regional Planning Commission
St. Charles Parish Environmental Council
South Central Planning and Development Commissin, Thibodaux
South Lafourche Regional Planning Commission
South Louisiana Tidal Water Control Levee District
State Soil and Water Conservation Committee
Terrebonne Parish Police Jury
Thibodaux Regional Planning Commission
Water Resources Study Commission
OTHER INTERESTED PARTIES
Center for Wetland Resources, Louisiana State University
Sport smens Committee, Morgan City Chamber of Commerce
Dularge Hunting Club, Inc.
Ecology Center of Louisiana
Orleans Audubon Society
Louisiana Center for the Public Interest
Louisiana Wildlife Federation
Howard Stark Company, Inc.
Student Activity for Environment, Nicholls State University
Woods and Waters Club
WVUE-TV
Individuals who requested copies of the document
LIBRARY INFORMATION CENTERS
Copies of this document were provided to the following libraries
Assumption Parish
Napoleonville, Louisiana
St. Bernard Parish
Chalmette, Louisiana
Jefferson Parish
Metairie, Louisiana
St. Charles Parish
Hahnville, Louisiana
Lafourche Parish
Thibodaux, Louisiana
St. Martin Parish
St. Martinville, Louisiana
Orleans Parish
New Orleans, Louisiana
St. Mary Parish
Franklin, Louisiana
Plaquemines Parish
Buras, Louisiana
Terrebonne Parish
Houma, Louisiana
6. COMMENT PERIOD
This draft environmental impact statement was transmitted to the
Environmental Protection Agency one week before the notice of
availability to the public appeared in the Federal Register . Comments
should be submitted to the Office of Coastal Zone Management within
45 days after the date of the Federal Register notice.
THE PROJECT AND ITS IMPACTS
SECTION 1: GENERAL PROJECT DESCRIPTION
A. SITE
The Port Fourchon development is a multi-purpose facility to be
completed on a 586 acre site located in the Tenth Ward of Lafourche
Parish, Louisiana, where the waters of Bayou Lafourche meet the Gulf of
Mexico. The project site lies within a larger tract of approximately
3,800 acres which is under the jurisdiction of the Greater Lafourche
Port Commission. The Commission was established in 1960, with full
powers of a port, harbor, and terminal district.
The site is located at the seaward end of the Lafourche trans-
coastal corridor, one of the most important and best established links
between the inland areas of the coastal zone and the Cull of Mexico.
This corridor is defined by Bayou Lafourche, an important water trans-
portation artery, and by alluvial ridges along the bayou (Fig. 1-1).
The Lafourche corridor forms a natural boundary between two major
estuarine complexes, the Terrebonne system to the west and the Salvador-
Barataria system to the east. Each of these systems is highly produc-
tive and represents a major resource (Fig. 1-2). To maintain the integ-
rity of these systems and provide for environmental management, these
systems must be retained as natural entities. Development related to
oil and gas industry and fisheries must therefore be concentrated to the
greatest extent possible on the higher boundaries of the units rather
than be allowed to disperse through canals, roads, and other hydrologic
alternatives with resultant fragmentation of the system. The Port
Fourchon development follows this principle in that it confines activi-
ties and related primary and secondary impacts to an existing corridor.
As shown in Fig. 1-3, the total tract is comprised of four major
components. Component A is the project area. Of the 586 acres lying
within this component, 55 acres will be occupied by the proposed
T-slip and 450 acres of spoil-filled area will be committed to other
aspects of the project development. Component B is an impounded wet-
land 2284 acres in extent. As shown in Fig. 1-3, an existing commercial
marina presently lies in the northeastern part of this component. Com-
ponent C is a 1316 acre area consisting primarily of wetlands bounded
by Belle Pass and Pass Fourchon on the west and east and by the Gulf
shore on the south. There is presently some petroleum industry related
activity in this component. Component D of the tract lies between Pass
Fourchon and Bay Champagne. Nicholls State University presently main-
tains a coastal and marine research laboratory in this component.
B. RELATIONSHIP OF THE PROPOSED ACTION TO THE TOTAL PROJECT
It is proposed that the fourth phase of a multiport facility be
implemented under the guaranteed loan provisions of the Coastal Energy
Impact Program. The facility will accommodate the needs of: 1) the
fishing and seafood industry, 2) recreation and tourism, 3) the offshore
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vessels are moored. Barges cannot be loaded to capacity and a reduction
of speed is necessary in order to keep wave wash to reasonable limits,
thereby preventing damage to moored vessels and structures. Movement
of large oil barges and drilling equipment over the bayou is exceedingly
difficult in the narrow waterway. On windy days, an extra tug is employed
in an effort to hold the tow straight and avoid collision damage. Con-
struction of the auxiliary channel would facilitate use of larger, more modern
vessels used in fish and oil industries and thus eliminate the need to
use circuitous routes by way of the Gulf Intracoastal Waterway (GIWW) .
b) General Design
General design features are as follows. The completed enlargement
of Bayou Lafourche would include a 9 ft by 100 ft channel from Lockport to
Larose, a 6 ft x 60 ft channel from Larose to Golden Meadow, a 9 ft x
100 ft channel from Golden Meadow to Leeville, a 12 ft x 125 ft channel
from Leeville to the Gulf, and a 20 ft x '300 ft channel from Belle Passe
to the 20 it contour in the Gulf. From Larose to Leeville spoil, would
be contained and effluent returned to tile waterway. from Leeville to
the Gull , spoil would be placed along the east bank ol bayou Lafourche
and be Lie bass.
The Bayou Lafourche auxiliary channel would be 30.4 mi long, 12 It
deep, and 125 ft wide. It would include a 12 ft by 125 ft stub channel toward
Golden Meadow with a turning basin 1300 ft long and 600 ft wide. Spoil
would be contained with retention dikes and spill boxes and effluent would be
returned to the dredged channels.
The Lafourche-Jump Waterway would provide a 12 ft x 125 ft channel.
Where traversing wetlands spoil would be retained along the banks of the
channel. Where traversing bays spoil would be placed on adjacent water
bottoms .
c) Site and Area Description
The action does not include specific facilities other than the loca-
tion of the channel which is given in Fig. 3-1. To achieve the objec-
tives of the proposed Port Fourchon facility it is anticipated that the
need for service to the fishing and offshore oil industry would be accom-
modated by increased use or expansion of existing docking facilities and
industries along Bayou Lafourche within the various communities.
Bayou Lafourche is a narrow coastal stream flanked by natural
levee ridges representative o[~ a development corridor. On
either side ai~ the corridor exist major, highly productive estuarine
complexes that grade from saline bays through saltwater, brackish water,
and freshwater marshes into freshwater swamps (Fig. 3-2).
Development along Bayou Lafourche includes agriculture on the wide
ridges north of Golden Meadow. Between Thibodaux and the Gulf there
are some fourteen communities with a total population of approximately
30,000. Toward the Gulf of Mexico communities are increasingly dominated
by economic activities that are related to the fishing industry and off-
shore services for the oil and gas industry. Continuous development ends
3-5
SALINE MARSHES - Typicol vegeiotr more than half of Louisiana's fisheries
production and through export of detrital material play an important
support role with regard to marine fisheries in the Gulf of Mexico.
Equally important is the role of these systems as breeding and nursery
grounds for shrimp and fishes. The marshes serve also as major winter-
ing grounds for migrating waterfowl.
Dredge and fill activities would destroy about 20,000 acres of
wetlands and water bottoms. Of these approximately 2000 acres lie
within the Point-au-Ghien Wildlife Management area and in the Wisner
Wildlife Management area in Terrebonne ana 1 Lafourche Parishes respectively.
The area encompassed by the Lafourche -Jump Waterway and auxiliary
channel include a number of archeological sites. At least six sites
would be directly affected and five sites are krjown to be present in
the immediate vicinity of the proposed routes.
Another major consideration is the effect of increasing salini-
ties through saltwater intrusion in the Lafourche auxiliary channel.
This effect would extend into the Gulf Intracoastal Waterway to the
extent that it would interfere with its use as an industrial and municipal
water supply for the city of Houma in Terrebonne Parish,
3. Beneficial Impacts
The Bayou Lafourche and Lafourche- Jump Waterway alternative
would provide more efficient and safer navigation into and out of the
area.
4. Decision on this Alternative
This alternative was rejected because of the severe nature of
adverse impacts on wetlands and related uses. Present losses of wet-
lands in Louisiana as a result of subsidence, saltwater intrusion,
channelization, spoil disposal, impoundment, and other actions affecting
water quality and the hydrologic regime amount to at least 16 sq
mi annually. These losses represent a cumulative impact that seriously
degrades the renewable resource base of the state and is of a magnitude
that may attain material significance.
3-8
C. STRUCTURAL ALTERNATIVE 2: WIDENING OF BAYOU LAFOURCHE
1. General Description of the Alternative
This alternative would provide for widening of Bayou Lafourche
from the Gulf of Mexico to the community of Larose where it intersects
with the Gulf Intracoastal Waterway.
a) Objective of the Action
The objective of this alternative action is to provide for safer
and more efficient navigation between the Gulf and the docking and
service facilities along Bayou Lafourche that support the fisheries
and offshore oil industry. Problems presently associated with naviga-
tion were described in Section 3, B, 1, a).
b) General Design
The project would require a channel 125 ft wide and 12 ft
deep.
c) Site and Area Description
The project would only provide for the widened channel. Increased
demand for services to the fishing and offshore oil industry would be
accommodated through increased use or expansion of existing facilities
in the communities along Bayou Lafourche.
See the first two paragraphs of Section 3, B, 1, c), "Site and Area
Description" for a description of the Bayou Lafourche environment.
d) Existing Use and Environment Physically Affected
See Section 3,B, l,d), "Existing Use and Environment Physically
Affected".
2. Adverse Impacts
Construction of the widened channel would result in a major change
in the environment. Many of the present service facilities are located
immediately along and partially extend into the waterway. These facili-
ties must be relocated. In many areas the road also follows the bank line
and widening of the channel would necessitate relocation of the road and
adjacent residences.
3. Beneficial Impacts
Construction of the widened channel would provide for safer and
more efficient navigation from the Gulf to the docking and service
facilities along Bayou Lafourche.
3-9
4. Decision on this Alternative
This alternative was rejected because of necessary relocations
of facilities, residences, and roads 3 and the associated adverse cultural
impacts. Due to the United width of natural levee ridges along Bayou
Lafourche, this action would also eliminate a large portion of the most
suitable existing land for development on one or both sides of the
bayou and would partially force development into adjacent wetlands that
bound the natural levee ridges.
3-10
D. STRUCTURAL ALTERNATIVE 3: REDUCING THE SCOPE OF THE PROJECT
1. General Description of the Alternative
This alternative would involve reducing the total scope of the project
with implementation of Phases 1 thru 5 only, Phases 1 thru 3, which have
already been completed, include limited docking facilities, a warehouse,
a marina, a boat launch, roads, utilities, and a stone jetty at Belle
Pass. Phase 4, under consideration for the immediate future, would include
dredging of the "T-Slip," preparation of 450 acres of spoil area for
facility sites with ditches and drainage structures, bank stabilization,
and dredging of the flotation canal and construction of additional bulk-
head for docking, Phase 5, to be implemented as the development progresses
and funding becomes available, would include the addition of a Police and
Administration Building, a sewage system ; and water mains and connections.
Completion of Phases 1 thru 5 would provide complete multi-purpose facilities
for steel-hulled shrimp boats, offshore survey and supply vessels,
smaller fishing boats, crew boats, and pleasure craft,
a) Objective of the Action
The main objective of this alternative would be to reduce the
ultimate size of the port and limit the kinds of activities that
would be located there, The port would be limited to handling fishing
boats, offshore service boats, and crew boats (including mineral extraction
industry and LOOP related activities).
b) General Design
The facilities designs, site location, and impacts for Phases 1
thru 5 have been presented in Section 1 , "Project Description" of this
statement .
Under the project proper, the only facilities are the "T-slip" and
adjacent sites, as described in Phases 1 thru 5 in Section 1, "Project
Description. "
c) Site and Area Description
This is treated under Section 1, A, of this report.
2. Adverse Impacts
Included in the two phases to be eliminated under this alternative
(Phases 6 and 7) would be the dredging of Belle Pass to 30 ft x 500 ft,
additional stone jetty improvements;, and additional bulkheading. Failure
to implement these phases would foreclose the option of larger ocean-
going vessels and repair and/or fabrication of large offshore drilling
rigs and platforms,
3-11
This alternative would limit the port's ability to respond to
future needs of the offshore mineral extraction industry. It would
also limit to a considerable extent the kinds and intensity of activi-
ties that would be conducted in the port area,
3. Beneficial Impacts
Restricting the channel depth and width would reduce the poten-
tial for saltwater intrusion and the rate of tidal exchange. This
would have the beneficial effect of reducing marsh deterioration and
erosion .
Physical effects on the environment, including streams and water
bodies for Phases 1 thru 5 have been discussed in Sections 6, 7 and 8
of this statement, The direct and indirect effects of dredging related
to the enlargement of Belle Pass including modification of benthic
habitat, temporary reduction in water quality during construction >
modification due to spoil disposal, and increases in saltwater intru-
sion and tidal exchange would be eliminated. In addition adverse
effects on water and air quality related to activities such as offshore
rig and fabrication yards would be eliminated.
4. Decision on this Alternative
The reason for rejecting this alternative is that it would foreclose
options for responding to future needs of the offshore mineral extrac-
tion industry.
3-12
E. NON- STRUCTURAL ALTERNATIVE 1
1. General Description of the Alternative
By reducing the amount of offshore energy activity in this area
the projected need for the port may be reduced. This could be partially
accomplished by reducing the rate of offshore leasing in the Federally
controlled areas of the continental shelf.
2. Impacts
This action would have the adverse impact of curtailing the national
supply of oil and gas. It would also have major economic effects locally
and regionally. This action would reduce traffic and product movement
through the coastal zone with proportional reduction of associated
primary and secondary impacts.
3. Decision on this Alternative
This alternative was rejected because it would not be feasible in
view of present national energy needs.
3-13
F. NON- STRUCTURAL ALTERNATIVE 2
1. General Description of the Alternative
Use of expansion of other existing small port facilities in the
region could be encouraged through legislative or financial measures.
2. Adverse Impacts
This action would have the adverse impact of increased boat
traffic through waterways in environmentally sensitive areas of the
coastal zone, as discussed under the "No Build" alternative. It
would also have local adverse economic impacts, Induced expansion in
areas of many existing ports would involve unmodified natural wetland
areas, Greater distance and travel time to work sites would be required
3. Beneficial Impacts
This action would have the benefit of concentrating expansion in
the vicinity of existing development.
4. Decision on this Alternative
The location of the proposed port at the end of the transcoastal
corridor and in proximity to the LOOP facility indicates that benefits
outweigh adverse impacts.
3-14
SECTION 4: PROJECT DESIGN
A. ENGINEERING DESIGN
The Port Fourchon project is a multipurpose facility designed to serve
as a port and industrial park. The port is to serve the offshore oil in-
dustry including the Louisiana Offshore Port (LOOP) for supertankers and
Outer Continental Shelf drilling, to provide docking, unloading, and repair
facilities for fishing boats, and to provide anchorage against Gulf
storms other than hurricanes. Docking facilities will be in a'T shaped
slip dredged into the port's property (See Fig. 1-3 in Section 1). Spoil
from the slip will be deposited in the southern one-third (450 acres)
of an impounded area to create sites for industries related to fisheries
and oil and gas exploration and development. Such industries may include
seafood processing industries, fabrication yards for offshore drilling
rigs, and boat repair yards. The engineering design to meet the Com-
mission's plans is summarized below in seven phases.
The firms of Picciola and Associates, Inc., and J. Wavne Plaisance,
Inc., under subcontract, conducted engineering invest igal iu us and studies
involving fieldwork, drafting, and calculations necessary tor the
dredging and widening of Bayou Lafourche and Belle Pass, the calcula-
tion of the amount of filled material made available by these operations ,
the resulting elevations of the fill sites, and the stimated cost of
these projects. The Division of Engineering Research, Louisiana State
University (Whitehurst, 1974a) studied the Belle Pass area in relation
to the proposed jetty system improvements and its effect on sediment
deposition and erosion along the area's shoreline. The study was spon-
sored by a NASA grant and by the Lafourche Port and Harbor Commission
grant for support of graduate students, 1974, and state funds from the
Division of Engineering Research, Louisiana State University. The
project phases are described below. Table 4-1 summarizes the cost and
status of these separate phases.
Phase 1 - Phase 1 has already been completed by the Greater La-
fourche Port Commission at a cost of $4.2 million. This phase consisted
of the deepening and widening of Belle Pass to a channel 20 ft by 300ft,
west of the existing channel from Mile 0.76 in Bayou Lafourche to a 20
ft depth in the Gulf of Mexico, and of a flotation canal which links
Bayou Lafourche with the commercial marina, making it accessible to
large shrimp boats. During this phase the commercial marina (with a
capacity of 68 large shrimp boats) was constructed, as well as a docking
facility and warehouse on Bayou Lafourche, a water distribution system
with a 300,000 gal elevated storage tank, and a five-ramp launch for
sportscraft. Other projects included in this phase were the construc-
tion of levees for flood and hurricane protection, the extension of
Highway 3090, and a bridge to provide access to the beach.
4-1
Table 4-1.
Development program for Port Fourchon.
Phase Description of Development
Cost
Status
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1 Construction of docking facili-
ties, warehouse, marina, boat
launch, roads and utilities
2 Stone jetty at Belle Pass
3 Roadway construction
4 A. Dredging
(1) Proposed slip "c"
(2) Belle Pass
2,700,000 cu. yds. of material
B. Stone jetty improvements
60,000 tons of stones
C. Drainage improvements
450 acres with ditches
and drainage structures
D. Flotation Canal
(1) Bank stabilization
4000 linear feet
(2) Dredging
292,000 cu. yds. of material
E. Bulkhead for docking
Total Phase 4 -
5 A. Police and Administration building
B. Sewage system
C. Water mains and connections
Total Phase 5 -
6 A. Belle Pass dredging 30 X 500
B. Stone jetty improvements
Total Phase 6 -"
7 Additional Bulkheading
$4,220,700 Existing
2,100,000
498,000
1,600,000
2,000,000
Existing
Under
construction
Planned
Planned
500,000 Planned
175,000
175,000
800,000
$5,250,000
181,000
812,500
206,250
$1,199,750
4,000,000
2,000,000
$6,000,000
2,500,000
Planned
Planned
Planned
Planned
Planned
Planned
Planned
Planned
Planned
TOTAL COST OF DEVELOPt-tENT - $21 ,768,450
Source: Greater Lafourche Port Commission, 1975
4-2
Phase 2 - This phase, completed in 1975, consisted of the improve-
ment of the small jetty at Belle Pass, extending it outward some 500 ft
into the Gulf of Mexizo. The jetty on the western side was extended a
distance of 2100 ft from the existing shoreline (see Fig. 1-4). Uork
was completed at a cost of $2,100,000.
Phase 3 - Phase 3, under construction at the present time at a
cost of $498,000, consists of a preliminary clam shell surface road
that will allow easy access to future industrial and commercial develop-
ment sites and to all port areas (Fig. 4-1, 4-2).
Phase 4 - The fourth phase of the development program, planned at
a cost of $5,250 ? 000, consists of:
a) Dredging a channel and slip and fill in Pass Fourchon left
descending bank, at a point about 1.7 mi above the mouth of the water-
way, approximately 8 mi southerly from Leeville, Louisiana, in Lafourche
Parish; and relocating and maintaining an entrance channel at Belle Pass
(20 ft x 300 ft). (Figs. 4-3, 4-4, 4-5).
b) Stone jetty improvements at Belle Pass (Bayou Lafourche).
(Fig. 4-5)
c) Flotation canal
1) Bank stabilization (Fig. 4-6 and 4-7)
2) Dredging
d) Drainage improvements
e) Bulkhead for docking
Phase 4, parts a, b, c, d and e have been granted permits from
the Corps of Engineers, New Orleans District, under Section 10 of
the Rivers and Harbors Act of March 3, 1899 (U.S. Congress, 33 U.S.C.
403, 1899); and under Section 404 of the Federal Water Pollution
Control Act (U.S. Congress, 86 Stat. 816, PL 92-500, 1972).
The dredging of the 20 ft x 400 ft slip (approximately 55 acres)
will produce two million cu yds of sand for filling approximately
450 acres, thus providing suitable foundation for future industrial and
commercial development. The fill material will be allowed to settle
before any type of construction commences. Drainage improvements to the
site so created will be undertaken during this phase, as part of its
preparation for development. Swale ditches dug with a small dragline
will be provided throughout the area.
Dredging will be primarily by hydraulic suction using heavy equip-
ment for most additional work. The dredge material will be pumped into
the area proposed to be filled, which is at present about 70% leveed
4-3
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400'
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eg
SPOIL AREA
EXISTING
GROUND
+ 2' MSL
-20' MSL
TYPICAL SECTION B - B'
SCALE: horz. V : 200'
vert. 1 : 30'
Fig. 4-2. Typical road cross sections at the Port Fourchon facility.
4-5
240+00
228+00
216+00-
204+00-
192+00
PAGNE
GULF
MEXICO
Fig. 4-3. Proposed channel and slip facilities at Port
Fourchon.
4-6
Pass Fourchon
AREA OF BANK TO
BE RESHAPED
PROPOSED
RIP-RAP
TYPICAL SECTION A - A'
i
Fig. 4-6. Proposed rip-rap at intersection of Bayou Lafourche and
the flotation canal at the Port Fourchon facility.
4-9
SPOIL AREA
PROPOSED RIP-RAP
TYPICAL SECTION A - A
SPOIL AREA
AREA OF BANK TO
BE RESHAPED
TYPICAL SECTION B - B'
5i—
FEET
10
Fig. 4-7. Typical sections of proposed rip-rap at intersection of
Bayou Lafourche and the flotation canal.
4-10
(levees were constructed at an earlier date), with a number of sluice
gates to allow water to run out from the site.
Bulkheading along Pass Fourchon is planned during Phase 4, to aid
the development of docking facilities and to prevent any further erosion or
washing away of the existing bank. The work will consist of the back
system with bumpers.
The stone jetty improvements will consist of adding stones over
the top of the stone jetty to increase its height, plus extending the
east and west jetty into the Gulf for a safer channel entrance and to
prevent rapid shoaling.
The work at the flotation canal consists of placing rip-rap along
each bank at its intersection with Bayou Lafourche and also on the south
side of the Fourchon Road. Some of the existing bank will be reshaped
as necessary for Lhe placement of the rip-rap. The dredging operation
will consist of removal of 330 cu yds of material to be deposited along
with approximately 360 cu yds of rip-rap along the project site shore-
line.
Phase 5 - Under phase 5 the Police and Administration building will
be constructed. A 12-in water main with all necessary connections
throughout the 450-acre development will be installed, and a sewage
system will be built. This system will provide for extended aeration
and tertiary treatment. Total cost of this phase will be $1,199,750.
Phase 6 - Belle Pass will be dredged to 30 x 500 ft and the stone
jetty will be improved.
Pha3e 7 - Phase 7 consists of additional bulkheading as required
to control erosional problems; the expected cost is 2,500,000.
Permits for Phases 5, 6, 7 have not yet been requested to the Corps
of Engineers. Applications will be submitted in due time, before any
construction work in these phases is undertaken.
4-11
B. ENVIRONMENTAL PROTECTION FEATURES FOR PROPOSED ACTION
The engineering design has taken into consideration the wetland
environment in order to minimize any adverse impacts which may result
from the project. The project is restricted to land which has pre-
viously been used as a spoil disposal area, with resultant loss of wet-
land habitat. Spoil will be deposited in a leveed, restricted area
which will not allow suspended sediment to spread across the adjacent wet-
land system. The banks of the canals will be stabilized by bulkheading
to prevent erosion by waves or runoff. Additional spoil will be dredged
from the adjacent, heavily traveled waterways in order not to modify
other wetlands.
C. ENVIRONMENTAL PROTECTION FEATURES FOR FUTURE PHASES
During Phase 5 of the project, a sewage system will be installed
and will provide extended aeration and tertiary treatment. This will
provide for minimal adverse effect of effluent on adjacent waters and
wetlands.
In Phase 6, the stone jetty will be improved to reduce deteriora-
tion of the channel. In Phase 7, additional bulkheading will be in-
stalled to control bank erosion. By establishing a designated indus-
trial zone, the port facility enhances cfentralization and industrial
development and reduces chances of dispersion of such development
through adjacent wetlands.
4-12
SECTION 5: COMPLIANCE WITH STATE AND LOCAL ENVIRONMENTAL
PERMITS AND PROCEDURES
A. STATE PERMITTING PROCEDURES
1 . Requirements
The State of Louisiana requires permits for a number of environ-
mental factors that may be associated with construction of the Port
Fourchon facility. These include: a) discharge into waters, b) emis-
sions into the air, and c) waste facilities.
a.) Discharge into Waters
If any type of activity will discharge waste into the state's
waters, a report to the Louisiana Stream Control Commission is required
before construction starts. The report is to describe the proposed dis-
posal system and the measures which will be followed to mitigate pollu-
tion. Construction cannot start before a report has been submitted and
granted a certificate of approval by the commission.
The report must contain: 1) a description of the proposed action,
2) location of the proposed action and exact location of the point of
discharge, 3) volume and concentration of waste to be discharged, 4)
description of waste treatment system to be installed, or measures that
will be taken to prevent pollution of the waters to be affected, 5) es-
timated quality of improvement of the waste by the proposed treatment
and measures that will be taken to control pollution, 6) an estimate of
the rate of flow of the receiving waters, 7) an estimate of the altera-
tion of the receiving water's quality by the proposed treatment work,
and 8) any other data pertinent to understanding the proposed action.
The report must be prepared and approved by a professional engineer duly
licensed in Louisiana.
The Louisiana Department of Public Health is responsible for deter-
mining if the coliform content of wastes discharged is within their cri-
teria of standards.
b) Emissions into the Air
If a facility will release matter into th,e air, a report must be
submitted to the Louisiana Air Control Commission through the Louisiana
State Board of Health. The report must be submitted before construction
starts and Should describe the proposed action and measures that will be
taken to protect air quality. The proposed construction cannot be
started before the report has been granted approval and a permit has
been issued by the commission.
5-1
The report should contain; 1) a description of the proposed
action, 2) location of the proposed action, 3) location of sources of
the emissions, the size of their outlets, the rate and temperature of
the emission, and the composition and description of the air contami-
nants being emitted, 4) description of measures for diminishing air
pollution that will be utilized, or any other methods that will be
used to prevent emission of undesirable levels of pollutants into the
air, 5) estimates of how much emissions from the proposed action will
alter the quality of the air, and 6) any other pertinent data for a
good understanding of the proposed action. The report must be prepared
and approved by a professional engineer duly licensed in Louisiana.
c) Waste Facilities
The Louisiana Health and Human Resources Administration requires
permits for construction of water supply systems, sewage systems,
and solid waste facilities that might be associated with the Port
Fourchon facility. The permit applications for these items should in-
clude complete construction and operating plans and sufficient engi-
neering data for project evaluation.
2. Status of Permits
The future phase waste treatment system has not been designed in
detail so a permit has not been applied for. There are no major emis-
sions into the air anticipated and so a report has not been filed. Per-
mits for water supply, sewage s /stems, or solid waste facilities asso-
ciated with the project have not been applied for. Prior to construction
all required permits will be obtained and all applicable procedures
followed.
In addition to permits, coordination with the agencies listed below
usually takes place in a project of this type.
3. Coordination with State Agencies
Louisiana Department of Transportation and Development - This de-
partment is presently developing a coastal zone program. The Greater
Lafourche Commission Development Program will be coordinated with state
Coastal Zone Management goals.
Louisiana Department of Public Works - The department may be called
upon to provide engineering services or advice and would be in a posi-
tion to insure coordination with other projects they may have in the
area.
Louisiana Wild Life and Fisheries Commission - The commission is
concerned about any adverse effects the loss of the study area
might have on fish and wildlife populations in both this area and in
5-2
adjacent areas. They strongly recommend that any activities in this
area be coordinated with them. The Port Fourchon area is currently a
research study area for the Wild Life and Fisheries Commission.
Louisiana Air Control Commission - There are not any special
air quality studies' in the immediate area being done by the commission,
They have not held any public hearings because of violation of air
quality standards by anyone in or near the study area,
5-3
B. LOCAL PERMITTING PROCEDURES
1 . Requir ements
The site is in the jurisdictional area of the South Central Planning
and Development Commission, the South Lafourche Regional Planning Commis-
sion, and the Lafourche Parish Police Jury. The planning commissions
serve as advisory and coordinating agencies. Powers of permitting rest
with the Police Jury.
2. Relationship with Local Agenci es
Contact with local agencies or governing bodies revealed the
following project relationships:
South Central Planning and Development Commission - On their present
"Land Use" map the Fourchon area is still represented as part of the
Wisner Wildlife Management Area, which it was, until it was deleted from the
map in October 1971. There is a study for a model zoning ordinance and
map for Ward 10, Lafourche Parish (where the Port Fourchon development
is located).
South Lafourche Regional Planning Commission - Their present zoning
ordinance map of Ward 10, Lafourche Parish, where the Fourchon Area is
located, is not presently in effect. According to Subdivision Regula-
tions Ward 10, Lafourche Parish, Louisiana, every subdivision of land
within the Parish of Lafourche excluding incorporated areas shall be
shown on a plot, and submitted to the Commission having jurisdiction for
review and recommendations and forwarded thereafter to the Police Jury
for grant or disapproval.
Lafourche Parish Police Jury - At a regular meeting on November 9,
1977, the Lafourche Police Jury adopted a motion stating that no identi-
fiable or potential conflict with any Jury regulations or proposed plans
were found in the development plans for the Port Fourchon facility.
(Parish of Lafourche Police Jury, 1977).
3. New or Additional Permits
Any new or additional permits or procedures that are developed
prior to construction will be obtained or followed.
5-4
SECTION 6: ENVIRONMENTAL SlfT-lARY
A. ENVIRONMENTAL PROBLEMS WHICH CANNOT BE SOLVED
L Land Constraints and Resources
The facility site is located in the low-lying coastal zone where
flooding from storm surge, high velocity winds, and torrential rainfall
occur in association with tropical cyclones and hurricanes. During the
hurricane season (late May to early November), the average number of
storms to cross this part of the Louisiana coast is 0.76/yr. Storm
generated floods may attain depths of 10 ft or more in the project
area.
The tract upon which the port site is located is surrounded by
relatively fragile, estuarine areas that are high in biological
productivity and are important from the standpoint of wildlife, fisheries,
and recreation.
There will be a direct land loss of approximately 55 acres due to
construction of the T-slip (Fig. 1-3). Approximately 450 acres of
marsh and old spoil areas will be filled with spoil material and con-
verted to industrial and commercial development. Some additional
land will be lost due to bank erosion from wave wash caused by pass-
ing vessels.
2. Vegetative Resources
Areas to be elevated by dredge material to 3.3 - 4.2 ft will be
transformed from a wetland habitat to a terrestrial area. The marsh
species (especially Spartina alternif lora and Avicennia ni^ida) will
be unavoidably and permanently lost from this site. Spoil-associated
species will be killed at the time and place of spoil deposition but
will regenerate once deposition ceases. Construction of roads, park-
ing lots, camp sites, and industrial areas will destroy any pre-existing
or emerging vegetation within the planned Port Fourchon facility.
Camping and recreation facilities near the beach will, in all
probability, destroy the present beach vegetation. This will occur
directly, through clearing, or indirectly, through trampling by heavy
tourist utilization of the area.
Areas behind the beach which are also scheduled for recreation
may eventually lose their existing vegetation either directly or as
a secondary consequence of vegetation destruction along the beach
front. Dune vegetation is noted for serving as a first line of defense
against wind and wave erosion and once removed, the coastal erosion
processes can proceed farther inland. This kills the interior vegeta-
tion by land erosion or saltwater intrusion. These processes will be
especially effective against the present and projected terrestrial veg-
etation which will occupy the higher spoil elevations required for the
development plan,
6-1
3. Wildlife Resources
Spoil coverage of the 450 acres to be developed will result in
a temporary loss of existing vegetated spoil bank habitat for rabbits,
small birds, and other animals which may occasionally utilize these
areas as a habitat. Revegetation of newly deposited spoil will occur
quickly, however, and spoil covered areas will have returned essentially
to previous conditions as far as vegetation is concerned within one to
two years after spoil is deposited.
Construction of roads, buildings, warehouses, and other structures
will permanently remove an area of spoil bank habitat over which they
will be erected. The general quality of spoil banks as wildlife
habitats will be reduced by the presence of structures, since activi-
ties of man and wildlife usage of an area are partly incompatible.
However, spoil banks are not prime habitat and are less ecologically
important than marsh habitats.
Some parts of the site, especially the Gulf shore, nearshore Gulf
areas, and the rock jetties at the mouth of Belle Pass, are used by the
brown pelican, Pelecanus occidentalis , an endangered species, as feeding
areas. Although this species would be the most affected by the project,
the area also serves as a habitat for two other endangered species, the
bald eagle ( Haliaeetus leucocephalus ) and the peregrine falcon ( Falco
peregrinus ) (Aycock, 1976) .
4. Water Resources
Turbidity increases due to the dredging and spoil placement will
temporarily affect the water quality of Bayou Lafourche and/or the
remaining brackish water environment within the impounded area. Pro-
bable but yet undetermined pollutional impacts will result from the
dredging itself and runoff from the disposal area. Dredging will
modify the water bottom of Bayou Lafourche and the flotation canal.
Salinity increase in Bayou Lafourche is unavoidable but salinity
increase of adjacent marsh environments could be ameliorated by res-
tricting water exchange through the limited number of tidal streams
that connect Lower Bayou Lafourche and Timbalier Bay.
There will undoubtedly be some water pollution derived from boat
traffic, minor spills or bilge-pumping, or from industries to be
located at the port. There is no way to assess the degree or nature
of water pollution from these sources during the pre-project period,
except to say that potential water pollution is likely to be of a minor
nature, since pollution regulations will be enforced. Water quality
standards of the State of Louisiana will be adhered to.
5. Aquatic Resources
Adverse effects on aquatic resources will occur during dredging
operations, consisting of destruction of benthic invertebrates living
in the bottom muds of areas to be dredged and temporary turbidity
increases caused by dredging which may affect primary aquatic production
6-2
for a short period. The areas to be dredged include a channel extend-
ing into the Gulf of Mexico from the Belle Pass jetties to the 30 ft
contour line, Belle Pass, Bayou Lafourche as far north as the flota-
tion canal, the flotation canal itself, and a T-slip north of Pass
Fourchon.
These losses are only temporary, however, Dredged areas will be
recolonized by bottom-dwelling invertebrates after dredging operations
are completed. Any decrease in primary aquatic production caused by
increased turbidities during dredging operations will be very short-term,
6. Economic and Social Impacts (Primary and Secondary)
Summary of Population Projections - Population projections for
the lower Lafourche Parish, and especially for Ward 10 where the
proposed facilities are located, are difficult to assess, since it
will depend to a great extent on such factors as construction of the
Superport off the coast of Bayou Lafourche and development of the
Port Fourchon facility. It is expected that since there exists almost
total employment in the parish, all direct employment will cause workers
to migrate into the parish (Gulf South Research Institute, 1974).
Future Economic Activity and Land Use - Loss of 450 acres of
spoil and marsh previously devoted to recreation, sport fishing, and
hunting will cause some monetary loss to the local economy, which
would be an unavoidable adverse environmental impact. Beneficial
effects are discussed at full length under Section 2,C of this report.
7 . Recreational Resources
The loss of 450 acres of recreational land to industrial and
commercial uses would be an adverse environmental effect which cannot
be avoided if the proposed project is implemented. However, additional
recreational land would be made accessible within the 3,800 acres at
Port Fourchon, including a large segment of sand beach. For additional
recreational benefits, see Section 6, B, 3 below.
8. Archeological Resources
Of the nine prehistoric archeological sites in the area, six could
be adversely impacted by primary effects of the project (Table 6-1) .
Included are sites 16 LF 7, 16 LF 82, 16 LF 83, 16 LF 84, 16 LF 85, and
16 LF 86, all of which could be covered by maintenance dredging spoil
(Table 6-2). Of these, sites 16 LF 82 and 16 LF 86 are considered to
be eligible for nomination to the National Register of Historic Places.
The remaining four are classed as slightly to moderately important;
all have some potential for yielding additional scientific data that
would contribute to a better understanding of the cultural history,
cultural processes, and paleoecology of the area.
6-3
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A-16
The Recent formation can be divided into seven depositional environ-
ments. All of these facies are common in a deltaic cross-section and are
distinguished by recognizable physical parameters (Table A-2). In the
study area only the natural levee and marsh environment are present.
Fringing the shoreline are reworked sand and shell beaches. Fig, A-2
shows the environments of the abandoned geomorphic features. Borings
which were taken in the study area by the U.S. Army Corps of Engineers
are shown in Fig. A-10.
Elevations along the natural levees of Bayou Lafourche range from
less than 5 ft MSL at Leeville to sea level at the mouth of Bayou La-
fourche. The brackish marshes in the interdistributary basins are at or
just above sea level. The marshes are inundated during high tides and
south winds. The Bayou Lafourche delta Complex has undergone subsidence,
consequently enlarging the bays, lakes, and marshlands in this area.
Subsidence rates for Louisiana coastal areas have been established
at 0.70 ft per century (Fig. A-ll) .
The present seaward edge of the Lafourche delta complex is one of
the most rapidly retreating parts of the Louisiana coastline. Retreat
rate estimates vary from 20 m to over 33 m per year (Morgan and Lari-
more, 1957) Gagliano and van Beek, 1970), The shoreline erosion rate
for the Port Fourchon area was recently determined to be in some places
2J.86 to 30.48 m per year (Whitehurst and Self, 1974). Figure A-12
shows historic and projected shoreline retreat in the Caminada-Port
Fourchon area.
2 . Subsurface Faults
Subsurface faults found near the study area are shown in Fig. A-ll
Surface expression is absent even though displacement along a single
fault may be as much as 2000 ft or more at great depths. Faults appear
to be related to the regional trend of the Gulf Coast Geosyncline.
3 . Salt Domes
Related to the thousands of feet of sediment in the Geosyncline
is the occurrence of salt domes (Fig. A-ll). The domes are cylindri-
cal masses of salt that pierce through sedimentary strata from a mother
bed at a depth of 20,000 ft or more. Economically, the salt domes are
important for various reasons. Associated with the upthrusting of the
salt stock, there is usually a peripheral upwarping of sedimentary
strata adjacent to the dome providing structural traps for hydrocarbons.
4. Econo mic Geology
In the vicinity of the study area and in the offshore areas the
principal geologic resources are oil and gas (Table A-3) . The areas
fronting the Lafourche Parish coastline contain 27% of the offshore
oil wells drilled and 12% of the offshore gas wells drilled in the state
A-17
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1961
SSSEESSsSJgnTOKWZSaWR
15-LD
1961
LEGEND
i§
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SILTY SAND
LEAN CLAY
17-L
1961
sss ^ agiaB ''^^^ l! sga , ag«
Fig. A-ll. Subsidence rates, subsurface faults, and salt domes
in the Port Fourchon area.
A-19
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A-25
LEGEHD
<5 PPT
5-10
10-15
15-20
20-25
>25 PPT
^^ MAJOR FRESHWATER INFLOW
C^ (BAYOUS, RIVERS, CANALS)
^">\ SECONDARY FRESHWATER INFLOW
(BAYOUS, CANALS)
^ MAJOR GULF INFLOW (CHANNELS,
^ PASSES)
tO Statute MHtes
tt Kilometer*
Fig. A-15. Average salinity distribution across
south .Louisiana (Continued).
A-26
Most important with respect to the project area is the interdis-
tributary basin formed by the natural levee ridges of Bayou Lafourche
and Bayou Moreau. This basin will hereafter be referred to as the
Fourchon Basin. Natural levee ridges of Bayou Moreau separate the
Fourchon Basin effectively from the Barataria-Salvador Basin to the east.
Natural levee ridges of Bayou Lafourche, on the other hand, are inter-
rupted in a number of places, thus connecting the Fourchon Basin directly
with Bayou Lafourche and indirectly with the Timablier Basin to the
west of Bayou Lafourche. Exchange of water with the Gulf of Mexico
occurs through one or more intermittent tidal passes connecting the
Gulf with Bay Champagne and Bay MarchandV, and indirectly and continu-
ously through Belle Pass and Bayou Lafourche.
Salinities of Bayou Lafourche are a function of a number of fac-
tors. These include: the introduction of freshwater from the Missis-
sippi River at Donaldsonville , salinity of water introduction through
canals connecting Bayou Lafourche and the Timablier and Barataria
Basins respectively, and Gulf water levels and salinities.
^ • Hydr ology of the Project Area
To discuss hydrology of the project area, the Fourchon Basin has
been divided into four smaller units shown in Fig. A-14, and numbered
one through four. Each of these units represents a hydrologic entity
with boundaries formed by natural and man-made features.
Unit 1 occupies the northern half of the Fourchon basin. Rigid
boundaries occur along the east and south sidej on the east is the
natural levee of Bayou Moreau and the associated road bed of LA High-
way 1 on the south side is a spoil embankment associated with the flo-
tation canal that connects Bayou Lafourche and a commercial marina.
To the west the unit is bounded by Bayou Lafourche; exchange of water
is possible through a number of tidal creeks. Spoil embankments along
Bayou Lafourche have led to partial ponding. The area is characterized
by the broken marsh surface and numerous shallow water bodies associated
with deteriorating salt marsh.
Unit 2 is part of the project area and is totally impounded by
spoil embankments and associated road beds except for one small outlet
to the flotation canal. Exchange of water with surrounding water bodies
is negligible. The area is almost entirely occupied by shallow waters.
As a result of impoundment, water has become brackish.
Unit 3 is a salt marsh basin bounded by spoil and an associated
road bed to the west and by the natural levee ridge of Bayou Moreau
to the east. Along the south side, it is bounded by a narrow beach
ridge which protects it from direct Gulf wave action but which allows
exchange of water through a tidal pass into Bay Champagne. The unit
represents an estuarine sub-basin within the Fourchon Basin. Most of
the area is characterized by salt marsh interspersed with numerous
small lakes and tidal channels. Bay Champagne takes up the remaining
area.
A-27
North-south water movement has been partly interfered with as a
result of the Chevron Canal, which is oriented east-west along the north
side of Bay Champagne. The canal connects with Pass Fourchon and thus
indirectly with Bayou Lafourche. At times, the tidal pass may be
closed due to spit building across its mouth. Under such circumstances
the Chevron Canal regulates water exchange.
Unit 4 is separated from the Gulf by a low marsh ridge that
occasionally is breached. Spoil embankments partly separate the area
from Belle Pass and Pass Fourchon with water exchange regulated by
intersecting location canals. Spoil deposition has resulted in
destruction of most of the original salt marsh. Some marsh remains in
the eastern half. Bay Marchand remains just inside the beach ridge
along the southern margin, but it is being filled as a result of
shoreline retreat. Since Pass Fourchon is closed at its mouth by a
dam, water exchange is primarily with water derived from Bayou Lafourche.
In general, the hydrology of Units 1 and 4 is regulated by condi-
tions in Bayou Lafourche that include stage, salinity, and water quality,
and by local precipitation and the degree of ponding. Unit 2 is an
impoundment, but subject to overflow during high tidal stages. Ponding
of local precipitation greatly reduces salinities. Unit 3 may shift
from indirect dependency on Bayou Lafourche when tidal passes are
closedj to direct exchange with marine waters when Bay Champagne is
connected with the Gulf of Mexico. Marine effects can be overriding
for all units when storm surges lead to flooding of the entire area.
3 . Major Tributaries
Only one major stream, Bayou Lafourche, affects the project area.
Bayou Lafourche originates at the town of Donaldsonville and flows into
the Gulf of Mexico. Originally a distributary of the Mississippi River,
the bayou was separated in 1904 from the Mississippi River by a dam;
water is now pumped into the bayou at rates from 100 to 300 cfs with an
average of 260 cfs. The length of Bayou Lafourche is approximately
102 mi. Water flow is confined between natural levee ridges but
artificial canals provide for exchange of water with adjacent estuarine
basins to the east and west. Near the Gulf of Mexico the channel
bifurcates into Pass Fourchon and Belle Pass. Pass Fourchon, however,
has been artificially closed so that all flow enters the Gulf through
Belle Pass. Belle Pass has been enlarged by dredging to a 20 ft by
300 ft channel to improve deep water access as part of the Port Fourchon
development program. Additional access work has been the building ol
jetties at the mouth of Belle Pass.
Bayou Lafourche can be separated into two reaches; An upper, fresh-
water reach from Donaldsonville to the Intracoastal Waterway, and a
lower reach from the waterway to the Culf which is subject to tidal
effects and saltwater mixing. The upper reach is dependent primarily
on water introduction at Donaldsonville and water exchange with the
Company and Intracoastal Canal. A weir at Thibodaux is for water supply
purposes.
A-28
Adjacent to the project area, Bayou Lafourche presently has a
depth of approximately 10 ft and a width of about 500 ft. The Bayou
has been intensively dredged for navigation, Dredging in the reach
from Leeville to the Belle Pass was completed in 1963 when a channel
of 12 ft by 125 ft was attained. Predicted maintenance frequency of
the section was ten years.
4 . Other Water Bodies Related to the Study Area
The study area relates indirectly to water bodies of the Timbalier
Basin as a result of linkage between the Bay and Bayou Lafourche.
Timbalier Bay and its fringing marshes connect with Bayou Lafourche
by means of Evans Canal and an unnamed pipeline canal farther north.
Both canals are shown in Fig. A-14.
5 . Uses of Surface Waters
Use of surface waters in the project area is limited to naviga-
tion related to oil and gas industry, commercial fisheries, and recre-
ation. The Bayou Laf ourche-Belle Pass channel serves as the main route
to the Culf of Mexico for fishing vessels stationed at the towns along
Bayou Lafourche. Many industries serving the well platforms in the
Gulf of Mexico are also located along Bayou Lafourche. The channel
further gives access to the Gulf for recreational activities such as
deep-sea fishing.
Within the project area, there are two more channels that serve
navigation. The flotation canal connects Bayou Lafourche with a
commercial marina adjacent to LA Highway 1. Pass Fourchon connects
Bayou Lafourche with oil and gas storage tanks.
6 . Stages, Flows, and Tidal Effects
Because of limited water input, stages in Bayou Lafourche and
connected waters of the project area are primarily determined by lunar
and wind tides. Average stages in Bayou Lafourche decrease in downstream
direction from 5.2 ft at Thibodaux, to 1.1 ft at Leeville to 0.4 ft at
Belle Pass. Near the mouth of Bayou Lafourche in the project area,
the stage variation averages 1.4 ft. Extreme conditions occur in
connection with hurricane passage or landfall. For example, stages
associated with hurricane Betsy in September, \9(> r >, ran to approxi-
mately 6.5 ft at the mouth of Bayou Lafourche.
Flows in Lower Bayou Lafourche are influenced strongly by wind
and tide. Connection with the Barataria and Timbalier estuaries
provide for discharge increases over the water input from the Missis-
sippi River at Donaldsonville . Flow measurements reported by White-
hurst (1974) are shown in Table A-4.
A- 29
Table A-4. Hydraulic data at selected sites.
Cross
Mile Sectional
Number Site Area (ft^) Q (cfs) max (cfs) V (fps) V max (fps)
106
3
565
266
544
0.471
0.963
70
14
750
266
544
0.394
0.725
51
22
1550
456
899
0.292
0.580
26
32
2930
533
4770
0.182
1.59
*A11 minimum flows are 0.0 cfs; All minimum velocities are 0.0 cfs.
(ft2)=square feet; Q (cfs)=adverse discharge, cubic fee_t per second;
Q max (cf s)=discharge maximum, cubic feet per second; V (fps)=adverse
velocity, feet per second; V max (fps)=maximum velocity, feet per
second.
Source: Whitehurst, 1974.
7 . Ti des and Wave Characteristics
Tides affect the coastal area by controlling the rate of mixing of
seawater and freshwater in this zone, influencing navigation depths in
the sea level canals, and regulating the rate of disposal of waste in
the coastal zone. Tides commonly inundate the lower coastal marshes to
depths of 12 to 29 in. On the average their speed varies up to 3.5 knots
during flood periods and up to 4.3 knots during ebb periods. The mean
tidal level is from 0.4 to 1.2 ft, and the mean tidal range is from 0.9
to 2.5 ft. Monthly data on tides along the central Louisiana coast
are shown in Table A-5. The normal tide along this coast is diurnal,
but strong winds may change its character. Winds modify the tides
significantly. During the winter months the marshes are rarely covered
as a result of northerly winds of long duration which accompany very
low tides. The lowest mean water levels occur from December through
March and the highest levels occur in September and October.
The Louisiana coast is known as a low-energy coast in terms of
offshore waves. Generally waves along this coast are 3 to 5 ft in
height with a period of 4.5 to 6 sec when wind speeds arc greater
than 10 km/hr. They commonly approach the coastline from the southeast
(Table A-6). A previous study (Becker, 1972) implies that during
spring and summer the intensity of offshore waves is at its lowest
peak but that during fall and winter it increases 2 to 3 times the low
intensity. Direction of approach and longshore current velocity are
important factors related to the erosion rates of the retreating shore-
line of the Port Fourchon area and should be taken into account when
considering the placement of structures for shore stabilization, hurri-
A-30
Table A- 5,
Monthly tide levels in feet along the Central Louisiana
Coast, 1958-59*.
Mean
Mean
Mean
Highest
Lowest
High
Low
Water
Individual
Individual
Month
Tide
Tide
Level
Tide
Tide
January
.39
-.35
.02
1.5
-2.0
February
.56
-.26
.15
1.6
-1.8
March
.60
-.18
.21
1.3
-1.5
April
.78
.09
.43
1.2
- .7
May
1.13
.40
.76
2.4
- .7
June
1.19
.18
.69
1.7
- .7
July
.83
-.06
.39
1.5
-1.0
August
.83
.11
.47
1.6
- .8
September
1.26
.69
.97
2.6
- .2
October
1.06
.39
.72
1.8
- .5
November
.85
.07
.46
1.5
-2.1
December
.37
-.62
-.12
1.4
2.2
Annual
82
.04
.43
2.6
-2.2
Source: *From Chabreck and Hoffpauir, 1962; Chabreck, 1972
cane protection, and navigational improvements. A recent report
(Whitehurst and Self, 1974) observed that littoral current moved from
east to west (waves approaching from east-southeast to southeast) .
Wave diffraction was also observed occurring around the jetty at Belle
Pass causing recession on the downdrift side and varying shoreline
recession immediately west of the channel.
The study concluded that shoreline erosion west of Belle Pass will
continue at the present rate from natural processes; and that the 1200
ft dike extension on the proposed west jetty will retard wave action on
the remnant island and at the mouth of the north-south canal to the
west. It also indicated that the proposed jetty s>stem will offer
safety to navigation in and out of Belle Pass at times of rough seas.
A-31
Table A- 6.
Annual wave climate summary for Coastal Louisiana,
Wave
Direction From Which Wave is Coming
Wave
Wave
Height
Period
(feet)
(seconds)
East
Southeast
South
Southwest
Subtotals
3.0
4.5
13.4%
20.9%
7.5%
5.0%
46.8%
5.0
6.0
8.9%
20.6%
8.7%
7.6%
45.8%
7.0
7.0
1.2%
1.2%
0.8%
3.2%
8.5
8.0
1.4%
0.5%
1.5%
0.8%
4.2%
Subtotals
24.9%
43.2%
18.5%
13.4%
100.0%
*The percentages cited are relative to portion of time during the year
when wind velocities exceed 10 kilometers/hour. Winds >10 kilometers/
hour prevail during 43.3 percent of the year on the average.
Source: Becker, 1972.
A-32
F. CLIMATOLOGY
The Port Fourchon area has a humid, sub-tropical, marine climate
associated with the latitude of the region and proximity of the site
to the Gulf of Mexico.
1. Temperature Distribution
The annual average temperature in the area is 69.2°F; the average
temperature in January being 54.9°F, and that of July 80.7°F. The
summers are hot with dominant southeasterly winds. Fall weather is
warm and generally frost free. During November frontal fogs begin to
appear, reducing visibility near the Gulf of Mexico. Winters are usu-
ally mild and cool; cold fronts, which move southeastward through the
area, are accompanied by high velocity northerly and northwesterly
winds. The average frost- free period is 264 days extending from Febru-
ary 27 to November 18. The greatest change in average temperature
between successive months occurs from March to April and from October
to November.
2. Rainfall Distribution
Precipitation is high, averaging 60.5 in annually (Table A-7).
July and August are the wettest months, with average monthly precipitation
means of 7.37 in and 6.63 in respectively. Generally the summer and winter
seasons are the rainiest. During the summer, moist Gulf air creates almost
daily afternoon and evening thunderstorms. Monthly precipitation means for
this season are 6.4 in. During the winter precipitation means are 5.2 in.
Rainfall during the spring is 4.6 in, slightly less than that during the
winter. Although autumn conditions regarding precipitation origins are
very much like summer, the monthly precipitation means are 4.5 in.
Precipitation is one of the most important environmental factors
in the coastal zone because it controls the area and amount of water
available (rainfall excess) for runoff into streams, lakes, swamps,
and marshes. Rainfall excess (precipitation minus soil infiltration
and evapotranspiration) for the study area expressed as a percentage
of annual precipitation is around 27 in (Fig. A-16). The mean annual
rainfall excess in the study area is 16 in (Gagliano et_ aj_. , 1973) .
3. Humidity
Humidity is high all yeararound but it is highest during the sum-
mer months because of abundant precipitation and because the prevailing
winds have a long fetch over the warm surface (Table A-8).
A-33
Table A-7. Monthly precipitation in inches (metric equivalents given),
Southeast Division.
Jan Feb Mar Apr May June July Aug Sept Oct Nov Dec
Monthly Average:
5.89 4.70 4.90 4.31 4.50 5.27 7.37 6.63 6.40 3.23 3.74 4.96
Monthly Average (cm) :
14.96 11.84 12.45 10.95 11.43 13.39 18.72 16.84 16.26 8.20 9.50 12.59
Winter (DJF) Spring (MAM) Summer (JJA) Fall (SON) Annual
Seasonal Average: 5.18 4.57 6.42 4.46 5.16
Seasonal Average (cm): 13.16 11.61 16.31 11.33 13.10
Source: Stone, James, et^ al . , 1973. ( v Data extracted and derived from
National Climatic Summary.)
«■
.
•
•
A-34
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A-35
Table A- 8.
Percentage frequencies of relative humidity observations
at 6 A.M. and 3 P.M. , during midseason months.
Relative
humidity
in percentage
0-29
30-49
50-69
70-79
80-89
90-100
January
6 A.M.
2
12
14
22
51
3 P.M.
4
25
42
12
9
8
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6 A.M.
2
9
7
22
59
3 P.M.
6
30
44
9
6
4
July
6 A.M.
1
2
20
77
3 P.M.
25 mph. October wind speeds continue to increase over
those of Sfptember, 13. 7% of which are >25 mph. The increase in wind
speed continues into the winter months showing December with 23.1% of the
winds being > 25 mph. Maximum wind speeds of over 120 mph generated by
cyclones and hurricanes can be expected in the study area from late May
to early November.
A- 36
Table A-9. Frequency in percent of winds from various directions in
the Gulf of Mexico; A. Monthly Data, B. Seasonal Data.
A. Monthly Data.
Jan Feb Mar Apr May June July Aug Sept Oct Nov Dec
N
19
13
12
10
10
4
4
4
6
13
18
12
NE
16
20
13
18
16
10
10
11
22
34
23
18
E
21
21
20
32
28
30
28
22
33
28
24
22
SE
17
17
27
19
17
23
18
13
13
7
11
16
S
7
10
12
7
6
6
10
8
5
2
6
8
SW
5
3
3
2
3
4
5
7
2
2
2
3
w
5
6
4
4
4
2
4
6
3
2
3
5
NW
10
10
7
7
5
4
4
5
4
4
7
7
B. Seasonal Data.
Fall Winter Spring Summer
18 16 10
21 27 27
17 21 18
9 6 4
Source: Stone, James, et al. , 1973 (Data extracted from U.S. Navel
Weather, 1970)~ ~
NE
26
E
28
SE
10
NW
5
A-37
G. FLOODPLAINS
Flooding in the study area is primarily the result of storm surge
from tropical storms. From late May to early November, tropical cyclones
and hurricanes may cross the area. These destructive storms flood
large areas of the marshes to depths of 10 ft or more. They cause severe
damage, and change the environment by raising the salinity of the marshes,
destroying wildlife habitat, and causing coastline erosion. During the
hurricane season, the average number of tropical storms is 0.76/yr.
The overall hurricane probability for any one day is 0,56% in June and
July and increases sharply to 0.99% during the early part of August.
The study area has been struck (in the period of recorded history) by
10 damaging hurricanes and 22 other hurricanes and tropical storms. The
paths of several of these damaging hurricanes are shown in Fig. A-17.
Flooding of the low lying areas at Port Fourchon occurs as a result
of the storm surges associated with cyclones, The highest stage of water
recorded for the area as a result of a hurricane was 9 ft above MSL at
Leeville (north of the study area) in September, 1915.
The area of inundation and conditions associated with the passage
of hurricane Betsy in September, 1965 is presented in Fig. A-18.
This illustrates how storm surge generation may cause direct flooding
as a result of inland propagation of the surge across the marshland,
and indirect flooding through upstream propagation of the surge on the
Mississippi River.
The proposed site is within the 100 yr floodplain as mapped for
U.S. Department of Housing and Urban Development in May 1971 (FIA, 1970).
The project is not presently specifically designed to minimize po-
tential harm to the floodplain, to meet flood-proof standards under the
National Flood Insurance Program, or to be in compliance with the Flood
Disaster Protection Act. The facility is however set back from the
beach area which creates a safety buffer consisting of a natural vege-
tation area.
A-38
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A-40
H. WETLANDS
With comnletion of Phase 1 of the Port Fourchon plan the natural
vegetation at the site is already undergoing significant changes.
Much of the 450 acres planned for development was formerly an inter-
tidal, regularly flooded saline marsh dominated by oyster grass ( Spar-
tina alternif lo ra) , a species which occurs in almost pure stands along
the Atlantic and Gulf coasts. In Louisiana marshes it is sometimes
associated with black rush ( June us roemerianus ) , black mangrove ( Avicen -
nia nitida ) , and saltgrass ( Distichlis spicata ) (Woodhouse , Seneca,
Broome, 1974; Chabreck, 1970; Penfound and Hathaway, 1938). Adjacent
to the low marsh were the more elevated and better drained narrow
levees and minor spoil banks along Bayou Lafourche, Pass Fourchon, and
Belle Pass. Terrestrial species including shrubs, herbs, and grasses
(Table A-10) occupied these landforms, but there were no large trees
(Tobin, 1940; Aero, 1951-52).
An oil tank farm and several small canals and rig cuts were con-
structed below Pass Fourchon in the early 1950's initiating a change
in the indigenous marsh vegetation. Some of the saline marsh was
covered by spoil material and shell which either remained bare or was
invaded by shrubs and grasses.
In 1967 approximately 2007 acres of this saline marsh were im-
pounded by levees and the area became progressively fresher as salt
water interchange was terminated (Monte, 1975). This resulted in
deterioration of the interior marsh since Spartina alternif lora required
flooding by saline water (Table A-ll). A large, shallow lake developed
in place of this marsh in the northern three-quarters of the impound-
ment. The lake bottom was invaded by Widgeon grass ( Ruppia maritima ) ,
while brackish to intermediated types of vegetation (Spartina patens and
Distichlis spicata ) began to replace the Spartina alternif lora along
the fringes of the lake.
Hurricane Carmen breached the levee in 1974 permitting saline
conditions to return temporarily, but the levees were repaired within
a few monLns. Had saline Gulf waters been allowed to resume circula-
tion in the impoundment, the Spartina alternif lora marsh may have re-
juvenated. However, under present conditions the impoundment will under-
go succession to an intermediate-to-freshwater lake and marsh environment
(Whitehurst, 1975).
The western and southern perimeter of this impoundment and the
land adjacent to Belle Pass and Pass Fourchon has been receiving large
amounts of spoil over the past 10 years. These spoil deposits ele-
vated the land mass, killed the established vegetation through silta-
tion, and initiated a transitional phase. Normal succession on these
spoil deposits is expected to culminate in a terrestrial species
association (over 60% not wetland species) , including some bottomland
hardwoods (Monte, 1976). By the time of field reconnaissance in
January 1976 a great diversity of species including shrubs, grasses,
and herbs already covered the spoil sites and only a few areas remained
unvegetated (Fig. A-19) . As expected, no vegetation grew in the pro-
ject area where the land had been paved with shell for roads, parking
lots, houses, and other industrial uses (Fig. A-20, A- 21, and A-22) .
A-41
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A-.43
Fig. A-19. Impounded area in Port Fourchon. Shrub grass,
herb community invading spoil deposited over
former saline marsh.
|_ .
Levee
High
Spoil
Low Spoil
Transitional
Marsh
Brackish to
Fresh Lake
I Shell
I Road
High Spoil
MARSH ELDER
EASTERN BACCHARIS
BEARD GRASS
GOLDEN ROD
RATTLE BUSH
WAX MYRTLE
SALT WORT
GLASS WORT
CATTAIL
WIRE GRASS
SALT GRASS
Low Spoil
GOLDEN ROD
SALT WORT
GLASS WORT
CATTAIL
ROSSEAU CANE
WIRE GRASS
SALT GRASS
OYSTER GRASS
Transitional
Marsh
SALT GRASS
OYSTER GRASS
Brackish to
Fresh Lake
WIDGEON GRASS
Fig. A-20. Schematic diagram illustrating morphological
environments and related vegetation associations
A-44
Fig. A-21. Spoil fill being prepared for Port
Fourchon development.
Fig. A-22. Port Fourchon beach. Erosion of the
shoreline is resulting in reworking of
the sand & shell beach and the destruction
of vegetation (black mangrove).
A-45
The beach along the southern perimeter of the Port Fourchon com-
plex is approximately 250 ft wide and consists of reworked sand^and
shell. This area is undergoing rapid erosion (Dantin, Vhitehurst,
Durbin, 1974; Fig. A-22). The beach material is being moved inland
by normal wave action and storm surges and is covering the interior
marshland, natural levees, and spoil sites. Small dunes back of the
beach are covered by beach grasses intermixed with the pre-existing
marsh and natural levee and spoil vegetation. A dense stand of
mangrove grows behind the beach adjacent to Pass Fourchon and along
the blocked tidal channel which bisects the southern portion of the
Port Fourchon complex. Scattered mangrove also occurs in the Spartina
alternif lora marsh surrounding Bay Marchand.
There are no direct economic or commercial uses for the vegeta-
tion in the vicinity of the planned complex. However, the marshlands
and estuarine areas are indirectly of great economic value. The exact
monetary value (of a marsh land) per acre is difficult to access,
although Cossalink, Odum, and Pope (1974) derived a figure of $4000
per acre per year "Based on the gross primary productivity (in energy
terms) of the natural marsh using a conversion ratio from energy to
do Liars based on the ratio of gross national product to national energy
consumption." The value of spoil bank vegetation has not been inten-
sively researched but it is believed to be approximately four times
less productive than a saline marsh (Young, Odum, Day, Butler, 1974).
In general, the vegetation of a salt marsh acts as an agent for
controlling erosion by absorbing and dissipating wave and tidal energy,
it also serves as a sediment trap, storm buffer, wildlife habitat, and
estuarine nursery (Lagna, 1975). Spartina alterniflora marshes are an
important component of any estuarine ecosystem for they possess high
rates of primary production, and provide for energy flow and nutrient
cycling.. Their annual primary production in southern climates such as
Louisiana is as high as 2960 g dry wt/m^/yr streamside and 1,484 g dry
wt/m 2 /yr 50 m inland. These high rates place the marshes among the most
productive systems on earth (Broome, 1973). Detritus washing from
these marshes constitutes one of the 5 major primary food sources for
estuarine organisms (Walker, 1973), many of which are ultimately
harvested by man. The extremely high primary productivity of Louisiana
marshland is largely responsible for this portion of the Gulf of
Mexico being called the "fertile fisheries crescent" (Gunter, 1967).
Louisiana's saline marshes are of value to fur mammals and water-
fowl in that they moderate the effect of tides and salinities. This
provides a buffer zone which protects the more desirable animal habi-
tats further inland (Palmisano and Chalireck, 1972).
The only direct recreation or aesthetic use for the vegetation
resources in this area would be by those who engage in collecting
plants or who wish to study an area undergoing dynamic changes resulting
from the actions of both man and nature. The well-developed grove of
mangroves along the beach and tidal channel and the beach vegetation
possess significant aesthetic value for those who appreciate this type
A-46
of environment. Port Fourchon provides one of the few easily accessible
areas for observing these particular associations along the Louisiana
coast; however, no rare or endangered plant species are known to exist
in this area (McGinnis, et al. , 1972). A list of the vascular plants
present in the area can be found in Table A- 12.
Table .A-12. A list of vascular plants present in the study area
Common Name
Scientific Name
Bushy beardgrass
Black mangrove
Eastern baccharis
Saltwort
Sea-oxeye
Flatsedge
Salt grass
Sandrush
Pennywort
Railroad vine
Marsh elder
Wax myrtle
Roseau cane
Palmetto
Glasswort
Glasswort
Black willow
Rattle bush
Sea purslane
Goldenrod
Oyster grass
Wire grass
Cattail
Andropogon glomeratus
Avicennia nitida
Baccharis halimifolia
Batis maritima
Borrichia frutescens
Cyperus sp.
Distichlis spicata
Fimbristylis castanea
Hydrocotyle sp.
Ipomoea pes-caprae
Iva frutescens
Myrica cerifera
Phragmites communis
Sabal minor
Salicornia bigelovii
Salicornia virginira
Salix nigra
Sesbania sp.
Sesuvium sp.
Solidago sp.
Spartina alterniflora
Spartina patens
Typha sp .
Source: Coastal Environments, Inc. field survey.
In summary, the study area serves as wildlife habitat for migra-
tory waterfowl and other wetland fauna (See Section 1, K). The Greater
Lafourche Port Commission has received three U.S. Army Corps of Engineers
permits as follows:
Date
Permit Number
Description of Action
October 7, 1974
LMNOD-SP
(Gulf of Mexico) 1242
Dredge Belle Pass to 20 ft
Install and maintain a jetty
A-47
Date
August lb, 1976
Permit Number
LMNOD-SP
(Pass Fourchon) 6
Description of Action
Dredge a channel and slip
Install and maintain a road
Fi 11 in Pass Fourchon
July 13, 1977
LMNOD-SP
(Bayou Lafourche) 702
Dredge in an area and install
and maintain rip-rap and fill
There is no state agency which permits activities in the wetlands.
The Louisiana Stream Control Commission, the Louisiana Air Control Com-
mission, and the Louisiana Health and Human Resources Administration
require permits for discharges into water and air and design of sanita-
tion facilities, but they do not control land use.
A-48
I. WILDLIFE HABITAT
1. Gener al Wild li fe Description
The Port Fourchon project area may be described as a modified
saline marsh zone at the mouth of Bayou Lafourche with a beach front on
the Gulf of Mexico. The marshlands in the project area have undergone
considerable change as a result of spoil deposition and impoundment.
A large area (approximately 2284 acres) of former marshland in the
northern two-thirds of the project area (above Pass Fourchon), which
formerly contained large marsh lakes (as shown on the 1953 U.S.G.S.
7.5 minute quadrangle) has been converted into a single, shallow,
impounded lake fringed with spoil deposits. A smaller marsh area (1300
acres) south of Pass Fourchon, vegetated mostly by oyster grass ( Spar -
tina alterni flora) and black mangrove ( Avicennia nitida ) , has likewise
been affected by spoil deposition, although the interior of this marsh
zone still receives tidal interchange with the Gulf via Bayou Lafourche,
the Tennessee Gas Transmission Canal, and small, natural channels. The
total area of functional marsh (approximately 600 acres) is, however,
small as compared Lo the modified areas.
Terrestrial wildlife habitats occurring in the Port Fourchon pro-
ject area consist of: 1) the Gulf beach, 2) saline marshes, and 3)
spoil deposits . Certain animal species utilizing these habitats may
be closely associated with one habitat type, while other species,
which are less exacting in their habitat requirements, may be spread
over all habitat types. Terrestrial wildlife species occurring in the
project area are discussed below under a) and b).
Aquatic habitats in the project include: 1) the surf zone of
the Gulf beach, 2) the jetties at the end of Belle Pass, 3) Bayou
Lafourche, 4) small canals and bayous arising from Bayou Lafourche and
entering the marsh, 5) the marsh proper, and 6) the large, impounded
brackish water lake along Highway 3090. Aquatic animals, including
fish and shellfish, and animals closely associated with or dependent
upon aquatic habitats, such as shore birds, wading birds, waterfowl,
and fur-bearing mammals, are the predominant fauna in the project
area which may best be described as an estuarine environment. Aquatic
animals occurring in the project area are discussed in more detail
below.
a) Game and Fur Mammals
Virtually the only game species of mammal occurring in the project
area is the swamp rabbit ( Sylvilagus aquaticus ) . Rabbit pellets were
numerous in both marsh and spoil bank zones in the project area, indi-
cating an abundance of swamp rabbits in these habitats. The Louisiana
Wild Life and Fisheries Commission, in a wildlife survey of Lafourche
Parish (1975), estimated the rabbit population in salt marsh habitats
as one rabbit per ten acres of marsh. It is not known to what extent
rabbits are hunted in the project area. The Wisner Wildlife Management
A-49
area (adjacent to the project area) has provided an average of 600
man/days of recreation in the form of rabbit hunting in past years
(Table A-13) .
Other game mammals, such as deer and squirrels, are absent from
the project area because of the lack of suitable habitat. The raccoon
( Procyon lotor ) is hunted as a game animal in forested areas of Louis-
iana, but it is unlikely that raccoon hunting occurs in the project
area.
Fur-bearing mammals which utilize salt marsh habitats include
muskrats ( Ondatra zibethicus ), nutria ( Myocastor coypus ) , mink ( Mustela
v ison ) , raccoons ( Procyon lotor ), and otters ( Lutra cana d ensis ). All
five of these species may occur in the project area. Although there is
some limited fur trapping in the area, salt marshes are not major trap-
ping grounds and most trapping efforts are carried out in other marsh
types (i.e., fresh, intermediate, and brackish marshes). It is also
in these other marsh types that the above-mentioned furbearers reach their
highest population numbers. Saline marshes may periodically contain
good numbers of muskrats, however, the quality of muskrat pelts (as
well as those of other furbearers) from salt marsh areas is low, a
factor which further reduces the value of salt marshes as fur-producing
areas .
b) Non-Game Mammals
No systematic survey of the non-game mammals of the project area
has been conducted. Terrestrial mammals which are likely to occur
here, however, include the nine-banded armadillo ( Pasypns nov emcinctus)
and the marsh rice rat (Oryzomys palustris ) . Certain bats, especially
the seminole bat ( Lasiurus seminolus ) , are probably nocturnal feeders
on insects over the marshes in and near the project area.
The Atlantic bottle-nosed dolphin ( Tursiops truncatus ) is common
in the nearshore waters on the Gulf of Mexico and inner bays near the
project area, and very likely enters Bayou Lafourche on occasions.
Other marine mammals may sometimes be observed offshore in the deeper
Gulf waters or found washed upon beaches. On August 19, 1939, following
a hurricane, Dr. George H. Lowery , Jr. of the L.S.U. Museum of Zoology
found A9 short-finned pilot whales ( Glohicephala macrorhyncha ) dead on
the beach 'several hundred yards west of Pass Fourchon on the delta
of Bayou Lafource' (Lowery, 1974b).
c) Game Birds
Waterfowl and rails are probably the only game birds occurring in
the project area in sufficient numbers to attract hunter interest. The
impounded, shallow lake along Highway 3090 appears to be utilized heavily
by waterfowl as a feeding area. This lake is also heavily hunted by
duck hunters in the winter months as evidenced by the large number of
A- 50
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Parish offshore waters arc among L ! u • most productive'
in Llie Gulf Coast for sports angling, due in part to the numerous
offshore oil and gas platforms. These platforms serve as artificial
reefs, attracting and concentrating many species of saltwater fish.
Several fishing rodeos arc held in the area from May to October.
Every August the three-day Tarpon Rodeo on neighboring Grand Isle
attracts thousands of visitors.
The only State Park near the Port Fourchon site is located on the
east end of Grand Isle, approximately 20 mi away. Grand Tsle State
Park, 140 acres, offers access to the Gulf of Mexico and a beach.
Jetties there can be used for fishing.
A 3 mi beach stretches from Bayou Lafourche to Bay Champagne
and offers opportunities for recreation. A small boat launch site has
been built with funds provided through a grant from the U.S. Bureau
of Recreation and is used by sportsmen in the area (see Fig. A-l) .
Hunting is another popular sport in the area since Lafourche
Parish has one of the finest hunting grounds in the state. The marshes
are wintering grounds for migrating wild geese and ducks. The hunting
season for both resident and migratory game opens in early September
and continues for about five months through the winter.
The Wisner Wildlife Management area is adjacent to the Port
Fourchon area. The 26,000 acres of the Wisner Wildlife Management
area are owned by the Wisner Donation Foundation and consist of low
saline marshes with dense stands of oyster grass. Hunted species at
Wisner are mainly waterfowl, rail, gallinule, snipe, and rabbits. Main
fish species are speckled trout, flounder, redfish, black drum, sheeps-
head, and croaker. Crabbing and shrimping are. also favorite sports for
the people in the area.
A-65
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C-5
Objectionable odors can be expected from the depostion of dredge
material on land due to decomposition of vegetation and organic materials
contained in the dredge spoil.. This would be a temporary effect which
could be expected to disappear in 2 to 3 months. A potential for objec-
tionable odors also lies in the anticipated fish processing industry;
however, this is considered a manageable source through control over
waste disposal.
C-6
SECTION D: WATER QUALITY
A. STATE WATER QUALITY STANDARDS
General and specific water quality criteria have been set for Bayou
Lafourche by the State of Louisiana. For Lower Bayou Lafourche, water
should allow primary and secondary contact recreation and should encourage
the propagation of fish and wildlife. Dissolved oxygen should not become
less than 4.0 miligrams per liter (mg/1), pH should be within the range
of 6.5 to 9.0, and the monthly total coliform median (MPN) should not ex-
ceed 70 per 100 and not more than 10 percent of the samples may exceed an
MPN of 230/100 mililiters (ml). No standards have been set for chlorides,
sulphates, and total dissolved solids (Louisiana Stream Control Commis-
sion, 1973). Because of salinity, Lower Bayou Lafourche does not serve
as a domestic or industrial water supply.
D-l
a. PRESENT CONDITIONS
The water quality of Bayou Lafourche relative to the project area
is first dependent on that of the Mississippi River and runoff from
towns, agriculture, and industries along the hayou, since the base supply
is obtained from shore sources. Changes in quality occur all along the
course of Bayou Lafourche as a result of development on its natural
levee ridges, exchange with water from adjacent estuaries, navigation,
and exchange with Gulf of Mexico waters. As a result of the changing
intensity of the processes that affect water characteristics in Bayou La-
fourche, a wide variation of physical and chemical properties is encoun-
tered in location and over time.
Water quality measurements are made by the U.S. Army Corps of
Engineers, New Orleans District, at two stations along Lower Bayou La-
fourche. These are located 5 mi below Leeville and at the mouth of Bayou
Lafourche. The project area is located approximately halfway between
those two stations. Water quality data \'^r Lower Bayou Lafourche are
shown i ii Tab 1 es D-l and I)- 2 .
Temperature in 1975 showed a natural fluctuation between a low
of 13.4°^ and a high of 32.2°G. No difference is apparent between the
two stations referred to, therefore temperatures shown may be considered
to be representative for the study area.
Conductivity expressed in 1000 micro-ohms/cm is approximately 20
percent higher at the mouth of Bayou Lafourche than at the station near
Leeville. This can be attributed primarily to higher salinities as a
result of proximity to the Gulf of Mexico. Conductivity measurements
vary greatly in Lower Bayou Lafourche. A study by Whitehurst (1974)
showed average conductivity variations of 10,000 micro-ohms at Golden
Meadow, 21 mi above the mouth of Bayou Lafourche.
Near the project area, continuous salinities are available for the
USCE gaging station at Leeville proper. Data from this station for the
period of 1962 through 1968 showed a mean salinity at mid-depth of 17.4
parts per tho (ppt) with a variance of 10.5 ppt. Salinities of Gulf
waters at the mouth of Bayou Lafourche are probably similar to those
measured at the Grand Isle mine platform and are mainly affected by
Mississippi River discharges. Salinities at mid-depth at the platform
over the period 1962 through 1968 averaged 26.1 ppt with a variance of
() -8 ppt. USCE data (USCE,, 197 2a) gives .i salinity range ol 23.4 to 2.8.8
ppt at the mouth o[ Bayou Lafourche.
Dissolved oxygen is invariably higher at the mouth o\ Bayou
Lafourche than near Leeville as a- result of greater turbulence and di
lution of Bayou Lafourche water with seawater. Average dissolved
oxygen concentration at the mouth of Ba w ou Lafourche was 7.5 mg/1 versus
6.8 mg/1 near Leeville. Even at the mouth of Bayou Lafourche, however,
oxygen content showed considerable variation, ranging between a low of
3.9 mg/1 in September, 1975 to a high oi 10.5 mg/1 in July, 1975. The
above readings show much improvement in water quality over conditions
further upstream. Above Mile 33, oxygen contents are barely above the
legal standard of 4 mg/1.
D-2
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D-4
Measurements of pH at the mouth of Bayou Lafourche and near Leeville
show 1975 averages of 8.1 and 7.6 . In both cases, variation is
wide, ranging between 4.0 and 9.6 near Leeville and between 6. 1 and 9.2
at the mouth of Bayou Lafourche.
Turbidity in Lower Bayou Lafourche is generally high as a result
of the shallowness and the great volume of traffic. Turbidation de-
creases, however, nearer the mouth because dredging u ?«? provided a deeper
channel and mixing with less turbid Gulf waters occurs. Jormal tur-
bidity levels in the vicinity of Golden Meadow are on the order of 25
JTU.
Nitrate and phosphate concentrations for Bayou Lafourche could only
be obtained as far south as Leeville. This is 5 mi north of the study
area where the Bayou connects with the estuarine system through the
southwestern canal. Average nitrate concentrations at this point were
0.87 mg/1. Average nitrate concentrations for Lower Bayou Lafourche
is on the order of 1.0 mg/1 (Whitehurst, 1974). Total phosphate values
along Bayou Lafourche fall rapidly south of Golden Meadow. Near Leeville
lolal phosphate- concentrations were 4.52 iii;-,/ 1 . These values most prob-
ably overestimate concentrations at the project area because of increased
mixing with Gulf of Mexico and estuarine waters.
D-5
C t ENVIRONMENTAL EFFECTS
1 , Water Temperature
No changes in water temperature are anticipated.. Although some
saltwater intrusion is expected as a result of channel enlargement,
water exchange processes between the project area and Gulf of Mexico
waters are such that this will not measurably affect the ambient tem-
perature conditions. Anticipated industrial development in the project
area does not include industries requiring thermal discharge.
2. Water Solids Content
Water solids content is expected to increase temporarily as a
result of increased suspension of sediments due to dredging, dredge ef-
fluent, dike effluent, and surface runoff. A temporary increase in tur-
bidity will result. Since much of the material will be sand and silt
with associated high settling rates, increases in turbidity will be of
short duration. Since flow in the Pass Fourchon and the flotation canal
is limited to tidal exchange, the areal extent of the turbidity in-
creases is anticipated to be limited mainly to those two water bodies.
The use of gates in the diked area will limit turbidity increase from
dike effluent.
Associated with the resuspension of sediments due to dredging and
spoil disposal, a temporary local increase in dissolved solids must be
anticipated. This increase, however, is not expected to adversely affect water
quality and biota. The majority of the spoil is produced through dredg-
ing of the 20 x 400 ft slip and involves deposits laid down more than a
thousand years ago. These sediments are unlikely to contain any toxic
substances. Redredging of Pass Fourchon and the flotation canal is a
repeat action that is not known to have produced unacceptable concen-
trations of dissolved solids since the project area is not subject to
industrial or other discharges containing heavy metals or other toxic
substances. A dredging permit has been granted by the U.S. Army Corps
of Engineers under Section 404 of the Federal Water Pollution Control
Act (U.S. Congress, 86 Stat. 816, 1972).
Anticipated future maintenance dredging also is considered not to
have long-term or severe short-term affects on water quality if adequate
measures are taken with regard to potential future industrial discharge
at the facility.
Permanent changes in solids content of the water may occur as a
result of further development of the area as a port facility serving
commercial fisheries and offshore oil industry. Road construction and
increased traffic will add road-associated pollutants to the water
through local runoff. Increased concentration of boats will add
D-6
pollutants of various sorts including oil and grease, ship garbage, and
trash fish. Oil and grease pollution can result from minor accidental
spills or bilge pumping.
Anticipated industrial development includes fish processing, boat
repair, and drilling rig fabrication yards. Two potentially serious
problems are associated with this, The first is the disposal of shell-
fish wastes, consisting largely of shrimp heads and shells. The second
is the potential introduction of toxic metals or acids associated with
materials used in fabrication of vessels and rigs. Whether this will be
an actual problem will depend on waste disposal and processing programs
and the degree of enforcement. Surface drainage design and treatment
of storm drainage and industrial waste water are considered feasible
measures to maintain acceptable water quality levels.
3. Nitrogen Saturation
No significant change in nitrogen saturation is expected if adequate
measures are taken for disposal of wastes and waste water from antici-
pated seafood processing industries. Sewage will be subjected to ter-
tiary treatment.
4 . Ha zardous Chemicals
On the basis of expected types of industrial development, discharge
of hazardous chemicals is not anticipated.
5. Pathogens
No significant change in pathogens is expected because of tertiary
treatment of sewage and limited increase of population in the project
area.
6. Kut rophica t ion
The nature of the project is not such that water impoundment or
temperature changes will be caused, and therefore will not change the
rate of eutrophication as a result of those possible causes.
7 . Taste and Odor
Provided that satisfactory methods are applied in potential dis-
posal of fish processing wastes, no taste or odor changes of the water
are expected.
D-7
D. WATER QUALITY CHANGES
Changes in water quality due directly to project construction and
maintenance are not considered to create conditions which are outside of
permissable or desirable conditions as expressed by water quality stan-
dards or general social opinion. Changes will not significantly modify
present conditions associated with existing levels of boat traffic and
existing docking facilities for commercial fisheries.
Changes in water quality due to future development will depend on
the nature of future industries. Whether the project will attract fish
processing industry and oil rig fabrication yards cannot be accurately
predicted. There will undoubtedly be some degradation of water quality
derived from boat traffic, minor spills, bilge pumping, and industries.
Yet the nature and extent of degradation is dependent on a large number
of elements that are unknown at the pre-project period. Major among
these are processing of industrial waste, discharge of surface water
drainage, monitoring and enforcement, and adherance to discharge permits
and criteria. Provided that the best available technology is used in
waste processing, that surface water drainage is not direcLly dis-
charged into adjacent waters, and that waste discharge standards are
adhered to, potential water quality changes are not considered to create
conditions that have an unacceptable adverse impact.
Relative to the above consideration, the construction of a tertiary
treatment facility subsequent to rather than commensurate with prepara-
tion for development under Phase A may be contrary to desirable control
over discharge of waste water.
D-8
SECTION E: WASTE WATER TREATMENT PLANTS
The project is not a waste water treatment plant. It contains a
waste water treatment plant as part of Phase 5 development. At such
time as it may be constructed, appropriate procedures will be followed
in its planning, design, permitting, construction a and operation.
E-l
SECTION F: SOLID WASTE MANAGEMENT
Under the remaining phases of the project a limited amount of solid
waste will be generated related to construction of necessary buildings
for administration and utilities. This will be primarily construction
waste, proper disposal of which will be the responsibility of the con-
struction contractor. These materials are expected to be removed from
the site by the contractor and disposed of according to state regula-
tion at designated sites, or will be disposed of in containers presently
available at the project site. Containerized waste is presently col-
lected twice each week by Sugarland Disposal, Inc., of Houma , Louisiana,
and waste is disposed of at a designated land-fill in Galliano, Louisiana
The container system also serves present docking facilities at the
commercial marina in the northern part of the project area. The system
is expected to be expanded to accommodate ship garbage associated with
future docking and terminal facilities along the proposed slips and
solid waste associated with occupancy of the planned administration and
utility building.
A potential indirect effect of the project is the generation of
waste related to the establishment of fish processing, rig fabrication,
and boat repair facilities. Because it will be the responsibility of
individual industries to dispose of solid wastes generated by such in-
dustry, and because the exact nature of future industries is unknown,
only limited predictions can be made at present as to future solid waste
generation associated with industrial development. In general, it is
expected that wastes that cannot be handled by the container system
will be shell fish wastes (shrimp heads and hulls) and metal such as
worn parts and fabrication remnants. It can be expected that metal will
be collected at the site and removed at intervals by truck or barge for
recycling.
Shellfish waste disposal is a problem at several locations along
Bayou Lafourche. No entirely satisfactory or economically feasible
methods of disposal have yet been found, although considerable moneys and
effort have been expended in search of such methods. Methods have
ranged from disposal in Bayou Lafourche to land application. No appa-
rent problems have resulted from disposal in Bayou Lafourche. Although
the shell fish waste increases the biological oxygen demand, the aquatic
ecosystem has not been streseed to the point that fish kills occur. A
major reason that adverse affects of such disposal are limited is that
much of the shellfish waste is consumed immediately by scavenging fishes
such as catfish.
F-l
SECTION G: HUMAN POPULATION
A. DESCRIPTION
Lafourche Parish is among the state's largest (1141 sq mi) and ranks
12th in population. In 1975 it had an approximate population of 72,028
with an average population density of 58.4 persons per sq mi, or a gross
density of 0.1 persons per acre. The majority of the parish population
is concentrated in a lineal development corridor on both natural levees
of Bayou Lafourche, the highest and most suitable land for residential
use. Net density, considering only the most desirable land, is much
greater than for the parish as a whole. The density of the developed
area of Lafourche Parish is 250.3 persons per sq mi. The residential
pattern for the parish is largely rural, with the city of Thibodaux,
the parish seat, representing the most urbanized area (14,925 in 1970).
Although the parish is rural in character, population increased at a
rate twice that of the State of Louisiana for the 1960-70 decade. For
the first five years of this decade the rate of growth for the parish is
almost five times that of the State of Louisiana as shown in Table G-l.
Table G-l. Population increases 1960-1970, Lafourche Parish and
Louisiana .
POPULATION GROWTH 1 Change
1960 1970 1960-1970
Lafourche Parish 55,381 68,941 +24.5
Louisiana 3,256,982 3,641,306 + 11.8
Source: South Central Planning and Development Commission, 1974a.
In 1970 the population composition of the parish was 89 percent white
and 11 percent non-white, or about the same ratio as that for the whole
United States. Between 1930 and 1970 the white population grew at a rate
of 2.1 percent as compared to 1.0 percent annua] growth I Or the non-white
population. This is probably because of a wide divergence of immigra-
tion rates. Population characteristics of Lafourche Parish as compared
to Louisiana in 1970 are shown in Table G-2.
G-l
Table G-2. Population characteristics of Lafourche Parish compared
to Louisiana (1970).
Lafourche
Population Parish Louisiana
1970 68,941 3,643,180
I960 55,381 3,257,022
Growth (Percent) 24.5 11.9
White
Number 61,041 2,541,070
Percent 89.0 70.0
Non-White
Number 7,900 1,102,110
Percent 11.0 30.0
Urban
Number 26,753 2,406,150
Percent 39.0 66.0
Rural
Number 42,188 1,235,156
Percent 61.0 34.0
Persons Per Square Mile 60.4 81.0
Source: U.S. Bureau of the Census, 1973
Projected populations for Lafourche Parish through 1985 (using the
cohort-survival technique), based on age, sex, and racial composition,
birth rate and death rate for specific age-sex-race groups, and net mi-
gration data, are presented in Table G-3.
Table G-3. Projected population - Lafourche Parish.
Projected Annual Projected Population
Year Projected Population Rate of Increase Density per square/mile
1970
68941
1975
71906
1980
75593
1985
79175
.85% 49
1.00% 51
.93% 54
57
Source: Burford and Murzyn, 1972
G-2
Population for Lafourche Parish and Ward 10 (the location of the
proposed development) for the years 1960 to 1975, and projected popu-
lations for the years 1980, 1985, and 1990 are presented in Table G-4.
Most of the population in this ward is concentrated in areas north of
the site. The only concentration of population in the vicinity of the
project is on Grand Isle, Ward 11 of Jefferson Parish; Grand Isle had
a 1970 population of 2,236.
Table G-4. Population Lafourche Parish and Ward 10,
Lafourche Parish Ward 10 % Parish
1960 55,381*
% change 24.1
1970 63,941*
% change 4.3
1975 71,906**
% change 5.1
1980 75,593**
% change 4.7
1985 79,175**
% change 5.0
1990 83,134***
% change
15,596*
28.1
20.7
-.7
18,831*
27.4
3.1
-.4
19,415***
27.0
5.1
20,410***
27.0
4.7
21,377***
27.0
5.0
22,466***
27.0
Source: *U.S. Bureau of the Census, 1973.
**Burford and Murzyn, 1972.
***Diversif ied Economic and Planning Associates, Inc., 1974
0-3
11. ECONOMY
Lafourche Parish is one of the most productive parishes in coastal
Louisiana. Its abundant hydrocarbon deposits and its estuaries comprise
.1 significant part of the stale's most productive resources. Bayou La-
fourche, the major inland waterway in the parish, provides the necessary
support for its future industrial growth. Its natural scenic beauty of
bayous, swamps, lakes, and marshes offers a unique setting for recrea-
tional opportunities.
The major commercial activities in the parish are agriculture and
fisheries, mining, manufacturing, transportation, communications, con-
struction, trade, finance, insurance and real estate, services and mis-
cellaneous, and unclassified establishments.
Employment is heavily concentrated around retail trade (20.1 "'),
closely followed by manufacturing (15.02%), and oil and gas extraction
(10.92%), (Table C-5). The total employment in Social Security con-
corned jobs was 11,916 for the first quarter of 1972; this does not in-
clude government employees, railroad employees, and self-employed persons
Payroll distribution IOi Lafourche Parish shows that transportation,
manufacturing (mainly food products), oil and gas, and retail trade, in
that order, are the principal contributors of taxable payrolls in the
par ish (Table 0-6) .
A comparison of t lie present distribution of employment by industry
division in Lafourche Parish, Louisiana, and the United States is shown
in fable 0-5. Lafourche Parish shows activity in transportation well
above the state and the national level, but lower levels in finance and
services .
I . Income
Lafourche Parish had its greater percentage of families earning
over $7,000 aid over $10,000 in 1969. It also had a smaller percentage
of people making below $5,000 and $3,000 than the state average (see
Table 0-7 and G-8) .
a) Agriculture
Although the character of Lafourche Parish is rural, only 66,789
acres (0.49%) of the total 786,594 acres"" are classified as agricultural
lands; this reflects the high percentage (65%)- of the land which is wet-
land and undeveloped. Agriculture mainly takes place in the northern
part of the parish; sugarcane is the principal crop.
'Discrepancies in total land acreage between these figures and those
shown above are due to different sources of information.
G-4
Tabic G-5 Percentage distribution ol employment by major industry
in Lafourche Parish.
LAFOURCHE PARISH 7///////////////////M
LOU T S 1 ANA #&&$&$&&&&
UN LIED STATES ^^^^
Industry
AGRICULTURE, ^/ 2.30
FORESTRY, AND £ 0.6
FISHERIES f 0.4
CRUDE OIL, CAS, '/ggg //// ////////////< ">•«
AND MINING Xv::;::;*:; 5.7j
ST 1.02
CONTRACT WML/to r'b
CONSTRUCTION frffiffij^^ f * **
MMMMMMl
MANLI FACTLI RING %&&&&&&&&&&$&&&&&&:
TRANSPORTATION W/////////////////////////MMM, 20.1
AND OTHER PUBLIC : 8&$8$&ffi^ 9.9
UTILITIES ^S^SS; 6.7
WHOLESALE TRADE W:%W:%¥:%W: 8.3
R ETA II, T RAD E ^^^^^^j^^m^^^j^^ 20.7
^^^^^^^ 20. 1
FINANCE, INS., %4## 4 - 3
ggg& ft! 8
S ERV 1C ES %¥*yffx*:^^ 18.3
UNCLASSIFIED ^f °" 9
ESTABLISHMENTS & 1 '°
ii 0.8
Source: Public Affairs Research Council, Inc., 1973; and
the Census, 1972.
0-5
L5.02
20.2
32.3
U.S. Bureau of
13. ECONOMY
Lafourche Parish is one of the most productive parishes in coastal
Louisiana. iLs abundant hydrocarbon deposits and its estuaries comprise
a significant part of the stale's most productive resources. Bayou La-
fourche, the major inland waterway in the parish, provides the necessary
support lor its future industrial growth. Its natural scenic beauty of
bayous, swamps, lakes, and marshes offers a unique setting for recrea-
tional opportunities.
The major commercial activities in the parish are agriculture and
fisheries, mining, manufacturing, transportation, communications, con-
struction, trade, finance, insurance and real estate, services and mis-
cellaneous, and unclassified establishments.
Employment is heavily concentrated around retail trade (20.1 %),
closely followed by manufacturing (15.02%), and oil and gas extraction
(10.92%), (Table 0-5). The total employment in Social Security con-
cerned jobs was 11,916 for the first quarter of 197'; this does not in-
clude government employees, railroad employees, and sel f-employed persons
Payroll distribution foi Lafourche Parish shows that transpor tation ,
manufacturing (mainly food products), oil and gas, and retail trade, in
that order, are the principal contributors of taxable payrolls in the
par ish (Table 0-6) .
A comparison of the present distribution of employment by industry
division in Lafourche Parish, Louisiana, and the United States is shown
in Table 0-5. Lafourche Parish shows activity in transportation well
above the state and the national level, but lower levels in finance and
services.
1 . Income
Lafourche Parish had its greater percentage of families earning
over $7,000 and over $10,000 in 1969. It also had a smaller percentage
of people making below $5,000 and $3,000 than the state average (see
Table 0-7 and G-8) .
a) Agriculture
Although the character of Lafourche Parish is rural, only 66,789
acres (0.49%) of the total 786,594 acres'" are classified as agricultural
lands; this reflects the high percentage (65%) of the land which is wet-
land and undeveloped. Agriculture mainly takes place in the northern
part o\ the parish; sugarcane is the principal crop.
'Discrepancies in total land acreage between these figures and those
shown above are due to different sources of information.
G-4
Tabic G-5
Percentage distribution ol em pi oynienl by major industry
in Lafourche Parish.
LAFOURCHE PARISH 71
LOUISIANA :%%
UNETED STATES ^mW\^
I/liifi...
^55^55^^
Industry
AGRICULTURE, ^^ 2.30
FORESTRY, AND xj 0.6
FISHERIES f 0.4
AND MINING XvXyXXy; 5 - 7j
ST 1.02
CONTRACT WMkmt, I'!
CONSTRUCTION \jsSS^ V ' ' %
MANUFACTURING
TRANSPORTATION WMMMZMZMMfflMZL 20.1
AND OTHER PUBLIC : $ffi&8&^$& 9.9
UTILITIES s>sSvNS^ 6.7
wmwL.
WHOLESALE TRADE &$^^£g% 8.3
^ffl'W" 7
X 20>1
R ETA 1 1 , TRAD E W?&&&&^ 20.7
X\\\\\\V\^\\\^^^ 20. 1
FINANCE, INS., Mlllkv.V. 4 * 3
AND REAL ESTATE i^W> 6 ' 3
S ERV 1 C E S : : : : : : : : : $a^a^a 1^^Si$iSSS 18.3
vmvvwwvvwvvwm 19.,
UNCLASSIFIED ^ 0>9
ESTABLISHMENTS & 1 '°
^ 0.8
Source: Public Affairs Research Council, Inc., 1973; and
the Census, 1972.
0-5
15.02
20.2
32.3
S. Bureau of
Table G-6
Payroll distribution in Lafourche Parish, Louisiana,
and the United States, January - March, 1972
(thousands of dollars).
Region
Industry
Lafourche
Parish
Louisiana
United States
Agriculture,
Forestry & Fisheries
Crude Oil, Gas
& Mining
Contract
Construction
Manufacturing
Transportation
& Other Public
Unclassified
Establishments
373
2,955
1,014
3,121
5,015
123,627
146,921
363,846
257,942
1,484,882
7,837,779
41,146,012
Utilities
3,886
152,841
9,381,966
Wholesale Trade
1,026
138,782
9,316,346
Retail Trade
2,557
193,561
14,094,066
Finance, Insurance
& Real State
862
93,847
7,655,764
Services
1,886
191,804
16,270,282
139
9,450
629,813
Total
17,819
1,419,694
Source: U.S. Bureau of the Census, 1972.
108,074,852
G-6
Table G-7
Families at various income levels, Lafourche Parish, 1969.
Families at Various
Income Levels
1959
Number % of Total
All families
Under $1,000
$1,000-$1,999
$2,000-$2,999
$3,000-$3,999
$4,000-$4,999
$5,000-$5,999
$6,000-$6,999
$7,000-$9,999
$10,000 and over
Income not reported
Below poverty level*
13,099
100.0
825
6.3
1,576
12.1
1,678
12.8
1,886
14.4
1,772
13.5
1,437
11.0
1,181
9.0
1,746
13.3
998
7.6
1969
Number % of Total
16,279
100.0
4 36
2.7
765
4.7
936
5.7
979
6.0
1,184
7.3
1,203
7.4
1,420
8.7
4,247
26.1
5,109
31.4
Not Available
2,511
15.4
Source: Public Affairs Research Council of Louisiana, Inc., 1973
Table G-8.
Percent of families with incomes under $3,000 and
$10,000 and over, Lafourche Parish, Louisiana and the
U.S.A., 1969.
Percent of Families With
Incomes Under $3,000 and
$10,000 and Over
Percent of Total
Under $3,000
1959 1969
Percent of Total
$10,000 and Over
1959 1969
Parish
Louisiana
United States
31.1
13.1
7.6
31.4
35.6
18.9
9.9
33.6
21.4
10.3
15.1
47.3
Source: Public Affairs Research Council of Louisiana, Inc., 1973,
G-7
Selected agriculture statistics for Lafourche Parish, Louisiana, are
shown on Table G-9. There is no agricultural activity in the Port
Fourchon area because the nature of the soils is not suitahle.
Table G-9. Selected agricultural statistics for Lafourche Parish,
Louisiana (1974 and 1969).
1974 1969
Number of Farms 356 519
Average Size in Acres 573 394
Percent of Area in Farms 27.9 28.0
Value of Land and Buildings Per Farm $108,349 $90,295
Value of Farm Products Sold ($1,000) 34,395 7,442
Source: U.S. Bureau of the Census, 1977.
b) Fisheries
The commercial fishing industry in Louisiana is among the largest
in the United States. In 1973, Louisiana led all states in volume of
landings. However, for the same year, Alaska led all states in value
of landings, followed by California and Louisiana. Commercial landings
of fish and shellfish in Louisiana were around 1.04 billion pounds,
valued at a record of $96.9 million (Table G-10) .
The principal commercial fish landing ports of Louisiana are at
Cameron, Dulac-Chauvin , Morgan City, Empire, and Golden Meadow. Golden
Meadow is just 20 mi north of the Port Fourchon area.
These ports were among the ten most active commercial fishing ports
of the United States, accounting in 1973 for landings of 329. 8 million
pounds of fish and shellfish valued at $60.11 million (Table G-ll) .
The leading species in Louisiana landings in the past five years were
shrimp and menhaden. In 1973 shrimp landings were 58.6 million pounds
valued at $44.5 million. In 1974 shrimp landings were 59.9 million
pounds valued at $52.1 million. Lafourche Parish ranks second only to
Terrebonne Parish in volume produce of shrimp along Louisiana's Gulf
Coast (Table G-12).
The third most valuable fishing in Louisiana is the oyster industry.
In 1973, oyster landings in the state were 8.95 million pounds of meat
valued at $5.5 million, representing an increase in both volume and
value over 1972 figures. In 1974, oyster landings were 8.9 million
pounds of meat valued at $5.7 million representing a slight increase
over 1973 figures.
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G-10
Table G-12. Volume of shrimp landings (Heads-Off Basis) reported
in Lafourche and Terrebonne Parishes, Louisiana
1967-1971.
Year Lafourche Terrebonne
1967 7,786,673 13,199,438
1968 7,165,628 10,937,655
1969 8,088,204 14,139,519
1970 9,902,675 15,629,867
1971 9,981,095 17,490,653
Source: Roy and Bordelon, 1974,
In 1971, 2,363,900 pounds of oysters were harvested in Lafourche
Parish; this represents the best year in quantity since 1964 and the
best year in value ($1,031,267). In 1964, 2,374,000 pounds were har-
vested with a value of $664,440 as shown in Table G-13.
Table
G-13.
Quantity and value of oyster landings, Lafourche
Parish, Louisiana, Selected years (1967-1971).
Year
Quantity (pounds) Value (Dollars)
1964 2,374,000 655,400
1965 96,000 29,100
1966 161,400 73,800
1967 630,900 198,039
1968 1,240,200 399,892
1969 733,500 319,112
1970 404,800 160,600
1971 2,363,900 1,031,267
Source: Stone, James, et al, , 1973.
The crab fishery industry is also important in Lafourche Parish.
It has tremendous potential for growth since this fishery resource is
bountiful in Louisiana waters.
Other species caught in Lafourche waters include buffalo fish, carp,
catfish and bullheads, flounder, drum, sea trout, snapper, Spanish mac-
erel, crayfish, squid, turtle, frogs, and many others. Combined, these
G-ll
species have a meaningful volume and monetary value within the fishery
resources. A large segment of the south Lafourche Parish population
is employed in fishing or seafood related industries. Average wages
and employment for Lafourche Parish in fisheries, canned and cured sea-
foods, and fresh or frozen packaged fish industries for selected years
are shown in Table G-14.
Table G-14,
Total and average wages and employment in fisheries;
canned and cured seafoods; and fish processing and
packaging industries in Lafourche Parish. Selected
years (1968-1972).
Year
Fisheries
1968
Employment
98
Total Wages
557,563
Average Wages
5,689
1969
Employment
94
Total Wages
586,119
Average Wages
6,235
1970
Employment
72
Total Wages
505,641
Average Wages
7,023
1971
Employment
103
Total Wages
643,223
Average Wages
6,245
1972
Employment
261
Total Wages
2,434,528
Average Wages
9,238
Canned and Cured Seafood
Fish Processing and Pack-
aging Industries
72
113,582
1,578
79
157,690
1,996
81
188,591
2,328
69
184,168
2,669
59
188,813
3,200
Source: Stone, James, et al. , 1973
Many of the fishery resources are estuarine dependent forms, there-
fore modification and destruction of marshes contributes to the decline
of these resources. This decline, in turn, affects the economy of the
parish and the state.
G-12
c) Mineral F.xtraction
The principal mineral resources in the study area are fossil fuels:
petroleum, natural gas, and natural gas Liquids. Sulphur is also mined.
For a number of years the extraction of crude oil and natural gas has
been a major industry in coastal Louisiana and has brought a number of
related petrochemical industries into the state. Fossil fuels are rap-
idly being depleted onshore increasing the need for offshore exploration
and production in order to meet the nation's energy demands. The volume
of oil and gas production for Lafourche Parish in 1970, when it ranked
third among the parishes in the state in the value of mineral production,
is shown on Table G-15 and G-16.
Table G-15. Oil and gas production in Lafourche Parish compared to
Louisiana (1970).
Crude Oil Condensate Cusinghead Natural
(Barrels) 3 (Barrels) 3 Cas b Cas b
(Mcf) (Mcf)
Louisiana (000) 787,138 117,699 1,104,941 6,691,805
Lafourche Parish (000) 117,674 8,272 138,586 296,994
Percent of Louisiana 14.9 7.0 12.5 4.4
a
b
42 Gallon Barrel; 15.025 pounds per square inch absolute.
Source: Louisiana Department of Conservation, 1972.
Table G— 16. Petroleum, natural gas, sulphur, natural gas liquid
(Minerals in order of value), 1973-1974.
1973 1974
Lafourche $439,940 $582,091
Louisiana $8,150,000*
* Louisiana, 96.4% of total mineral production value was crude oil,
natural gas, and natural gas liquids.
Source: Louisiana Department of Conservation, 1976.
G-13
Production figures for offshore areas fronting the Port Fourchon
area, when compared to Louisiana offshore totals, represent 31.5 percent
of the total production and account for 8.5 percent of the state total
tax revenue derived from offshore operations (Table G-17).
As indicated before in Table G-5, 10.92 percent of the total work-
force in the parish representing a payroll of $2,955,000 was involved
directly in mining operations in 1972. Indirectly there are many jobs,
such as construction and transportation activities, associated with the
petroleum industry.
d) Manufacturing
Included In manulaetur Lug are: food and kindred products, sugar,
raw cane sugar, cane sugar refining, paper and allied products, paper
mills (excluding building paper), machinery (excluding electrical), farm
machinery, transportation equipment, and ship and boat building and re-
pairing. Manufacturing accounted for 1,790 employees in the first quarter
oi 1972 in the parish. This represents 15.02 percent of the total 11,916
persons employed at the time. Manufacturers in Lafourche Parish and in
the area around Port Fourchon are shown in Table G-18.
e) Retail and Wholesale Trade
The retail and wholesale trade segment of the economy accounted fur
:,231 jobs, 27.1 percent of the estimated work-force in Lafourche Parish
for the first quarter of 1972.
f) Services
Services employed 13..20 percent of the work force in the parish in
the first quarter of 1972.. This section accounted for the lowest paid
job in the state; the average weekly wage was $91 in 1972.
g) Economic Growth
Projections of economic growth are somewhat difficult to assess
because of the many variables involved and unpredicated changes that
might occur in the area.
Mineral resources, on which a large segment of the economy is
dependent, are rapidly being depleted posing a danger to the parish of
becoming more economically depressed. The development of the superport
off the mouth of Bayou Lafourche could, on the other hand, mean more em-
ployment opportunities resulting in additional parish income (Gulf South
Research Institute, 1974). The development of the Port Fourchon facility
is another factor which would economically contribute to the growth of
the parish.
G-14
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GUNBOAT LANDING
MARKSVILLE
HOPEWELLIAN-
MARKSVILLE
200 A.D.
MAGNOLIA
MANDALAY
£ i
^ ?-■-■
SMITHFIELD
LABRANCHE
JEFFERSON
ISLAND
I /
: t
BEAU MIRE
TCHULA
TCHEFUNCTE
250 B.C.
LAFAYETTE
GRAND LAKE '
PONTCHARTRAIN
POVERTY POINT
1000 B.C.
GARCIA
BEAU RIVAGE
POVERTY POINT
BAYOU JASMiNE
RABBIT ISLAND
o
LATE ARCHAIC
PEARL RIVER
COPELL
BAYOU BLUE
<
3000 B.C.
o
ce
<
MONTE SANO
MIDDLE ARCHAIC
ARCHAIC
AMITE RIVER
BANANA BAYOU
?
EARLY ARCHAIC
ST. HELENA
?
9
LATE PALEO
PALEO-INDIAN
JONES CREEK
VATICAN
STROHE
o
i
EARLY PALEO
?
AVERY ISLAND
?
-1
PRE-PROJECTILE
POINT
?
?
?
?
?
J-3
analysis would seem to confirm this, except for the "Mound ville types''
and Fatherland incised which connote a later Mississippi period occupa-
tion.
16 LF 8 - No data.
16 LF 9 - No data.
16 LF 34 - Mclntire gives this site an initial occupation during
the early Mississippi period. Table d - 2 supports this statement.
Percentages of decorated sherds for two sites in the
Port Fourchon area, 16 LF 7 and 16 LF 34.
Table J- 2
SHERD
16 1
,F 7
7
.5%
22
.5%
35
.0%
15
.0%
16 LF 34
Fatherland Incised
Moundville Types
Fort Walton Types
Manchac Incised
Plaquemine Brushed
Unclassified Decorated
20.0%
15%
15%
65%
5%
Source: Mclntire, 1958
Newman (1973) also briefly mentions each of these four sites. He
describes each as a shell midden and gives tentative dates to three of
them:
16 LF 7 - Baytown to Plaquemine culture.
16 LF 8 - Coles Creek to Mississippian .
16 LF 34 - Plaquemine culture.
Finally, Philip Phillips (1970) in his monumental work on the lower
Mississippi Valley mentions two of the Port Fourchon area sites. He
places 16 LF 7 and 16 LF 34 into the Bayou Petre phase of the Mississippi
period .
J- 4
D. TYPES OF SITES AND LOCATION
In addition to the above mentioned four sites, the archeological
survey conducted for this impact statement, by means of pedestrian and
boat search, revealed five new sites in the Port Fourchon area (Fig,
A-2).
The following summary is derived from all of the sites, both newly
discovered and previously reported:
1 6 LF 7 - This site is located immediately west of the west jetty
of the Belle Pass channel (29 o 04»55 u N Lat., 90°13'44"W Long. - NE 1/4
of NW 1/4 Sec. 34. T.23S, R.22E). The site has been destroyed by wave
action and shoreline retreat. When first reported, it was listed as
beach wash. During this survey no evidence, aside from scattered oyster
shells, was observed along the beach west of Belle Pass. Currently,
spoil deposits are being dumped onto the beach so that any further at-
tempt at locating scattered sherds or stone would probably prove fruit-
less.
16 LF 8 - This site is located along the beach bordering the Gulf
of Mexico in front of Bay Marchand (29°05'37"N Lat., 90*12 * 005"W Long. -
Center of Sec. 26, T.22S, R.22E). The coordinates originally delin-
eating the site location were 29 t '05'15"N, 90 c 12' 05"W, and would place it
about 2,000 ft out in the Gulf from the present shoreline; there is
probably an error in the original coordinant location. Again beach
retreat has played havoc with the site. During the course of this
survey only two sherds were collected along the beach at Bay Marchand
and represent what is left of a midden formed on the Lafourche delta
farther out in the Gulf.
16 LF 9 - This site is located east of Pass Fourchon (29*06' 23"N,
90°10'18"W - Sec. 7, T.23S, R.23E) along the beach between the pass and
Bay Champagne. The original location (probably in error) is listed as
29°05'49"N, 90°10'35"W. The site is in the same state of preservation as
16 LF 7 and 8, and only wave-washed artifacts may be expected. Nothing
was found by the survey team.
16 L F 34 - This site is located along the east bank of Bayou
Lafourche (29° 12' 50"N, 90°13'35"W - SW 1/4 of NW 1/4 of Sec. 3, T.22S,
R.22E). It was located when canal dredging revealed its presence.
Mclntire described it as a series of small middens on the natural levee
of Bayou Lafourche. This survey's crew did not visit the site, but it
is listed as "destroyed" by the Louisiana Archaeologic Survey and Anti-
quities Commission.
16 LF 82 - The site is situated on the west bank of Belle Pass
(29*05' 50"N, ~90'13 f 50"W - south central portion of Sec. 2?, N-Central
portion of Sec. 27, T.23S, R.22E), and extends for approximately 1.4 km
along the bank. The site was found during the course of the CEI survey,
and can be described as a wave-washed oyster shell midden. No evidence
J-5
of in situ material could be seen. The site is about 0.3 to 0.5 in high
and about 3-6 m in width. Much ceramic material was obtained and ana-
lyzed.
16 LF 83 - This is another oyster shell midden, similar to 16 LF 82,
but it is located on the west bank of Bayou Lafourche (29° 07 '40"N , 90°
13'07 n W - SW 1/4 of SE 1/4 of Sec. 10, T.23S, R.22E). It ranges from 6-9 m
in width and is about 15 m along the bank. The site is totally wave-
washed with shell and much pottery is scattered along the banks.
16 LF 84 - Although tentatively recorded as a site this location is
at a pipeline crossing on the west bank of Belle Pass (29 U 06'12"N, 90°
12'30"W - E 1/2 of NW 1/4 of Sec. 23, T.23S, R.22E). A lengthy (about
300 in) pile of Rangia euneata shells has been placed along the bank to
help shore it up, and these Rang i a arc definitely not part of a midden.
However, sherds washing out of the Rangi a shells were located along the
northern portion of the pipeline crossing. Also associated with the
sherds, but minor in comparison to the amount of Rangia, were oyster
shells. The oysters and the artifacts may be eroding from a midden pres-
ently covered over by the Rangia pile. Another possibility is that the
Rangia used for the pipeline crossing were removed from another Indian
midden, at some unknown location, and transported along with the sherds
to the bank of Belle Pass.
16 LF 85 - The CEI survey located a small (10 m long by 1 m wide)
oyster shell midden on the south bank of the small bayou which courses
through the marsh between Belle Pass and Pass Fourchon. The site is lo-
cated at the confluence of the bayou and Belle Pass (29 c 06 ' 30 :: N, 90°12*
05"W - S 1/2 of MW 1/4 of Sec. 23, T.23S, R.22E). The mouth of the bayou
has since been silted in, however, so the site appears to be located on
a little cove along the east bank of the pass. The site appears to be
wave-washed, with only a few in situ material remains.
16 LF 86 - Immediately across Belle Pass from the northern portion
of 16 LF 82 the survey party located a badly disturbed oystershell
midden (29 C 06'11"N, 90°12*55"W - SE 1/4 of SE 1/4 of Sec. 22, T.23S, R.
22E). This midden lies to the north of a slip dug for an oil well lo-
cation, along the east bank of Belle Pass, and has an extent of approx-
imately 30 to 40 m and a width of about 15 or 20 m at its widest point.
The midden cannot be seen from the pass, and was only located hv walking
back from the pass's bank.
Two levees have been constructed over the western portion of the
site and run parallel to each other and to the bank of the pass. A
small canal (assumed to be a pipeline canal) lias also been dredged
through the site, with the spoil deposits from this canal adding to the
levees. It was the artifacts and oysters washing out of the levees which
first brought the site to the attention of the survey team. To the east
of the canal cutting through the site, a large area could be seen con-
taining scattered oyster shells and artifacts; however, dense marsh
grass prevented determination of this area's exact dimensions. From
J-6
what was seen, the area extended back from the large, westernmost levee
for about 15 or 20 m. No measurements as to the depth of this deposit
could he determined, but the midden in this area seems to be in situ.
In addition to these prehistoric archeological sites the CET
survey located the remains of a shrimp boat washed up on the beach
fronting Bay Marchand. Although a shrimp boat is of little archeo-
logical value, its widely scattered wooden remains are interesting and
may be a popular place for beach parties or campers.
J-7
E. STATUS
It may be emphatically stated that sites 16 LF 7, 8, and 9 are
totally destroyed, with only slim bits of evidence for their presence
remaining. Site 16 LF 7 is currently having spoil deposits from Belle
Pass dumped upon it, so it is doubtful that it will yield any further
information. Sites 16 LF 8 and 9 may contain some highly wave-washed
artifacts, but their scientific study potential is small.
16 LF 34 was not visited by the CEI survey team; however, it lies
well beyond the project area.
16 LF 82 and 83 are wave-washed sites with little to offer
strat Lgraphically , but much to offer materially. They are fine col-
lecting areas for artifacts and the data which can be gained from hori-
zontally controlled collection of such artifacts should prove extremely
beneficial. They are most highly important for that reason.
16 LF 84 is so small and wave-washed that it is questionable how
much in! oi nu t ion c:\\\ be gained from if. However, the fact that it is
completely reworked has not been confidently established, and in situ
artifacts and midden may still remain. If that proves to be the case,
a high priority should be given to the site.
Finally, 16 LF 86 may prove to be the most significant site in the
area. Aside from the western portion which has been dredged and leveed,
the remainder of the site appears to be in fairly good condition. Al-
though surface artifacts were not very plentiful, there may be more ma-
terial still in place below ground. The site is also very important in
thai it may have been the camping area for Indians who utilized the Belle
Pass region. The aerial dimensions of the site suggest such a possi-
bility. The site is also immediately across the pass from 16 LF 82, and
thus some definite relationship between the two is highly probable.
J-8
F. GENERAL HISTORICAL INFORMATION
The historical role of the Bayou Lafourche area centers around the
bayou's use as a main artery for transportation and commerce in south-
eastern Louisiana, connecting the Mississippi River with the Gulf of
Mexico and the many towns along its flanks to one another. The entire
Lafourche area was settled by Spaniards, by Germans from the German
coast, and by Acadians from Canada in the eighteenth century. The
Acadian influence is the most strongly reflected in the present day pop-
ulation. The name Lafourche (the fork) is one testimonial to French in-
fluence; it is derived from the configuration in which the bayou flows
from the Mississippi River at Donaldsonvil le . In 1904, this flow was
cut off by the partial construction of a lock and dam system intended to
control flood waters. A pumping station was finally built in 1955,
allowing the bayou to once again distribute Mississippi River waters.
The flanks of the bayou are extremely fertile and have been farmed from
the earliest days of its settlements. Sugarcane farming is especially
productive and this activity is a viable part of the landscape and the
lifestyle in the area.
Bayou Lafourche was also active during the Civil War as it was
recognized for its wealth and closeness to New Orleans.
The nearest known historic sites are the Cheniere Camanada, lying
approximately 4 to 5 mi east of the proposed port site, and Jacko Bay
Camp, 5-2 to 7 mi to the northwest. According to Swansea (1975), the
settlement at Camanada may date to the Spanish period in Louisiana when
Fort Blanc was established in that area. The settlement prospered in the
early 1800' s when sugar plantations thrived in the area. Before the
severe hurricane of 1893, Cheniere Camanada was heavily settled by fish-
ermen with a population of about 2,000 people, the most populus area
along the Louisiana Gulf shore at the time. Over 1,000 people were
drowned in the storm of 1893 and the community was largely abandoned
until the 1930's when a highway was built into the area.
Jacko Bay Camp was a fishing and hunting settlement located around
two small bays on the northeast shore of Timbalier Bay. Twenty-seven
structures are shown on the 1894 edition of the U.S. Geological Survey,
Timbalier, Louisiana quadrangles. The structures were probably all
built above the marsh level on pilings.
Neither o\ these historic sites is within the near-vicinity of the
proposed port facility. The sites will not be adversely impacted by the
proposed project.
J-9
G. EVALUATION OF SITES
The results of the survey and study were reviewed with representa-
tives of the SIIPO and I he Greater Lafourche Port Commission.
Of the historic and prehistoric sites known to exist in the general
vicinity of the proposed project, four represent possible candidates for
nomination to the National Register of Historic Places. These are the
Cheniere Camanada settlement, Jacko Bay Camp, Site 16 LF 82, and Site
16 LF 86. The first two are historically significant, while the latter
two prehistoric sites have in s itu material and potential for contrib-
uting significant information to culture history, cultural processes^ and
paleoenvironmental conditions of the area.
Possible adverse effects could occur at six of the prehistoric
sites as a result of the project if precautionary measures arc not taken.
Sites 16 LP 7 and 16 LP 86 could be affected by spoil disposal. While
16 LP 7 is already so badly degraded and of such minor importance that
protect ive measures are not warranted, Site I 6 LP 86 is ol Nat ional Reg-
ister caliber and will be excluded from designated spoil disposal areas.
Pour sites on the west bank of Belle Pass (16 LP 82, 16 LP 83,
16 LF 84, and 16 LF 85) might be endangered by future disposal of spoil
resulting from maintenance dredging. This adverse impact will be
averted by designating the sites as non-spoil areas.
As in most cases, secondary impacts related to accelerated erosion
and vandalism, which may affect the form of the sites (16 LI'' 82, 16 Id' 1 83,
16 LF 85, and 16 LF 86), are more difficult to deal with. The sites are
too large and erosion too far advanced for structural measures, such as
rip-rap or bulkheads, to be effective. Instead, a program of systematic
data and artifact collection to be conducted over a period of years has
been recommended . Survey monuments or reference points will be
established (in places safe from erosion), and systematic surface collec-
tions and observations will be made at least once a year. The collecting
will be controlled by area and referenced to the survey monument. In
the event that special features are exposed by erosion, they will be
systematically excavated and recorded.
The program will be conducted by qualified archeologists and the
data deposited in the custody of the Louisiana Archeo 1o ( j, ical Survey,
Department o\' Culture, Recreation and Tourism.
J-10
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