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Land Use Report Phase I south centrol plonni 9 I n L n, a C May 1980 deve ooment commission P.O. BOX 846 THIBODAUX, LOUISIA.NA 70301 ~0 ~1p~652;144;16;88q!~2p~856;224;36;20q-~2p~~~~~~~ATA ~. No. 2. 3. ~ ~ ~~~~~ 'I, A C C ~ 0. SHEET 4. Title and Subtitle ~S. Report Date May, 1980 LAND USE REPORT: PHASE 1 6. 7. Au~hor~q(s~q) ~q8. Pc~qH~orm~ing Organization Rcpt. Edwin J.~*Durabb, ~q@P~qroject Director No. 9. Performing Organization Name and Address ~10. Proi~ect/T~ask/Wo~rk Unit No. South Central Planning & Development ~6qG~0qm~qy~qnission P.O. Box 846 ~q1~q1. Contract/Grant No. Thibodaux, Louisiana 70301 ~q(~q:~2qPA~-~2qLA~-06~-48~q-1090 12. Sponsoring Organization Name and Address 13. Type of Report ~& Period Louisiana Department of Urban and C~qc~n~0q=ity Affairs Covered Office of Planning and Technical Assistance Final 1979~-1980 5790 Florida Boulevard (P.O. Box 44455) 14~. Baton Rouge, Louisiana 70804 1~5. Supplementary Notes N/A 16. Abstracts This.. report provides base data on land use and land over in the South Central Planning & Development Com~nission district available to local planners and local government officials. ~7. Key Words and Document Analysis. 17~c. Descriptors N/A 17~b. Id~entifi~er~s/~qOp~en-End~ed Terms N/A 17c. COSATI F~qi~qeld/G~qr~qo~qup 18. Availability S~qt~qa~qt~qe~qr~qn~qen~qt~: 19~q.. S~qec~qj~q. icy Class (This 21. No. of ~qPa~qs~qe~qg~q; South Central Planning & Development Co~6qm~6qn~6qission ~0qR~qep~qo~qr~qc~2q@ 199 ~0qU\~q'~qC~q-~q1-~q@~8qS~20qa~qW~0ql~4qF~qr) I ~6q- 20. Security Class (This 22. Price Page U ~qN C I F I ~qE D FORM ~qNT~q1~q5~q-3~q5 (REV. ~q10-73~q? ENDORSED BY ANSI ~qAND LIN ~qE~qS~qC~0qO. THIS ~qF~q0~q1~q0~q-~q1 MAY BE REPRODUCED ~qu~qs~qc~qo~qm~qm~q-~q;~2q@~qC ~q.~q2~q.~q@~q,~2q-7~q. LAND USE REPORT: PHASE I For The SOUTH CENTRAL PLANNING AND DEVELOPMENT DISTRICT Prepared By SOUTH CENTRAL PLANNING & DEVELOPMENT COMMISSION THIBODAUX, LOUISIANA THIS REPORT WAS PREPARED UNDER CONTRACT CPA-LA-06-48-1090 BY SOUTH CENTRAL PLANNING & DEVELOPMENT COMMISSION. THE PREPARATION OF THIS REPORT WAS FINANCIALLY AIDED THROUGH A COMPHRENSIVE PLANNING GRANT FROM THE DEPARTMENT OF HOUSING AND URBAN DEVELOPMENT, AND THROUGH THE ASSISTANCE OF THE STATE OF LOUISIANA, DEPARTMENT OF URBAN AND COMMUNITY AFFAIRS, AND BY SOUTH CENTRAL PLANNING & DEVELMENT COMMISSION. Property of MAY 1980 U S DEPARTMENT OF COMMERCE NOAA COASTAL SERVICES CENTER 2234 SOUTH HOBSON AVENUE CHARLESTON, SC 29405-2413 SOUTH CRURAL PLANNING & DEVELOPMINr COWISSION, INC. POLICY BODY COMPOSITION NAME (BY PARISH) REPRE,=ING TITLE ASSUMPTION Gilbert Dupaty Minority Citizen Interest Businesman Ridley P. Guillot Police Jury Police Juror Floyd Labarre Town of Napoleonville Mayor Elvin Simoneaux Police Jury Police Juror LAFOURCHE Jervis Autin Town of Golden Meadow Town CounciLnan Sondra Barrios Town of Lockport Director, ODA Earl J. Brown Minority Citizen Interest Businessnan Ronald Callais Police Jury Police Juror Irving Legendre, Jr. Police Jury Police Juror John Robichaux City of Thibodaux Mayor ST. CHARLES Philip Cortez Police Jury Police Juror Clayton Faucheaux Police Jury Police Juror Curtis Johnson Police Jury Police Juror COMMI SS ION M@MERS (Cont d) NAME (BY PARISH) REPRESENTING TITLE ST. JAMES Pep Detillier Police Jury Police Juror Whitney Hickerson Police Jury Police Juror Dale Hymel, Sr. Town of Gramercy Town Councilman Paul Keller Police Jury Police Juror Guy Poche Town of Lutcher Town Councilman ST. JOHN THE BAFrIST Dick Sorapuru Police Jury Police Juror Brent Tregre Police Jury Police Juror Richard Wolfe, Police Jury Police Juror TERREBONNE Howard Dion Minority Citizen Interest Businessman Donald Landry Police Jury Police Juror Eduard Lyons City of Houna, Mayor Ray Marcello Police Jury Police Juror Ernest Moss Minority Citizen Interest Businessman Blake Pitre Police Jury Police Juror ORGANIZATIONAL STAFF CHART FUI.I.r-TIME STAFF Ba.rry Brupbacher - Executive Director Edwin J. Durabb - Director of Planning/HUD Planner Cheryl S. Breaux - Section 8 Administrator/HUD Regional Planner Mike Strausser - CDBG Grant Administrator Jim Edmonson - Director of Grant-,qnmship and Program Development Irwin Fingerman - CZM/208/Solid Waste Planner David House - EDA Coordinator Marcia Shaffer Public Information Specialist Jessica Chenier Bookkeeper/Accountant Betty Maggio - Executive Secretary Ka.ren Weaver - Secretary Jo Anna Moore Secretary Sarrmy Campbell Student Intern PART-TIME EMPLOYEES Joe Horan - Executive Assistant Gwen Galiano - Secretary Mary Vaughn - Librarian (will not be employed by July 1, 1980) Janice Till man - Secretarial Assistant STUDENTS Ray Babin - Drafting Jody Chenier - Draftino, t> Clyde Harmer - Accounting PROJECr SrAFF PROJECT DIRECIIOR Edwin J. Durabb - Director of Planning CO=IBUTING AUIHORS Dr. Paul Leslie - Nicholls State University Irwin Fingennan - CZM/208/Solid Waste Planner, SCP&DC Jim Edwnson - Director of Program Development and Grantsmanship, SCP&DC DRAFTING Ray Babin - Head Draftsman Jody Chenier - Assistant Draftsman EDITING AND GRAPHICS Marcia Shaffer Public Information Specialist Edwin J. Durabb Director of Planning TABLE OF CONTENTS LIST OF TABLES . . . . . . . . . . . . . . . . . . . . . . ... LIST OF FIGURES . . . . . . . . . . . . . . . . . . . . . . . . vi PLANNING AREA OF SOUTH CTZ?rRAL PLANNING I AND DEVELOPMENT COMMISSION . . . . . . . . . . . . . . . viii INTRODUCTION . . . . . . . . . . . . . . . . . . . . . . . . . 1 PART I - THE NATURAL =ING CHAPTER I - CLIMATE. Introduction . . . . . . . . . . . . . . . . . . . . . . . 4 Terrperature . . . . . . . . . . . . . . . . . . . . . . . 6 Winds . . . . . . . . . . . . . . . . . . . . . . . . . . 16 Air Quality . . . . . . . . . . . . . . . . . . . . . . . 17 Bibliography . . . . . . . . . . . . . . . . . . . . . . . 23 CHAPTER 2 - GEOLOGY Introduction . . . . . . . . . . . . . . . . . . . . . . . 24 Economic and Structural Geology . . . . . . . . . . . . . 30 Sunnary . . . . . . . . . . . . . . . . . . . . . . . .32 Bibliography . . . . . . . . . . . . . . . . . . . . . . . 34 CHAPTER 3 - GBDMORPHDLOGY Introduction . . . . . . . . . . . . . . . . . . . . . . . 35 Recent Geologic History . . . . . . . . . . . . . . . . . 37 Recent Alluvial Processes . . . . . . . . . . . . . . . . 40 Sumk,u-y . . . . . . . . . . . . . . . . . . . . . . . . . 47 Bibliography . . . . . . . . . . . . . . . . . . . . . . . 50 CHAPTER, 4 - SOILS Introduction . . . . . . . . . . . . . . . . . . . . . . . 57 General Soil Types . . . . . . . . . . . . . . . . . . . . 53 Bibliography . . . . . . . . . . . . . . . . . . . . . . . 56 CHAPIER 5 - NATURAL VEGETATION Introduction . . . . . . . . . . . . . . .. . . . . . . . . 57 Forested Areas . . . . . . . . . . . . . . . . . . . . . . 58 Non-Forested Areas . . . . . . . . . . . . . . . . . . . . 61 Mixed Areas . . . . . . . . . . . . . . . . . . . . . . . 69 Surmary . . . . . . . . . . . . . . . . . . . . . . . . . 71 Bibliography . . . . . . . . . . . . . . . . . . . . . . . 73 CHAPTER 6 - DRAINAGE AND GROUNDWATER RESOURCES Introduction . . . . . . . . . . . . . . . . . . . . . . . 74 Drainage Basins . . . . . . . . . . . . . . . . . . . . . 75 Bibliography . . . . . . . . . . . . . . . . . . . . . . . 95 CHAPTER 7 - THE WEILANDS ECOSYSTEM Introduction . . . . . . . . . . . . . . . . . . . . . . . 96 Sediment . . . . . . . . . . . . . . . . . . . . . . . . . 97 Wetlands . . . . . . . . . . . . . . . . . . . . . . . . . 97 Detritus . . . . . . . . . . . . . . . . . . . . . . . . . 98 Water . . . . . . . . . . . . . . . . . . . . . . . . . . 98 Living Organism . . . . . . . . . . . . . . . . . . . . . 98 O-ther Properties of Estuaries . . . . . . . * * , , , , '99 A View of the Ecosystem of the Estuarine Basin . . . . . 101 Bibliography . . . . . . . . . . . . . . . . . . . . . . 110 PART I I - LAND USE CHAPTER - POPULATION AND SETTLENINT PATIERNS General History . * * * , , , * * * * , * * * , , , * , ill Settlemnt Patterns . . . . . . . . . . . . . . . . . . 117 Bibliography . . . . . . . . . . . . . . . . . . . . . . 124 CHAPTER 2 - AGRICULTURE History . . . . . . . . . . . . . . . . . . . . . . . . 125 Sugarcane . . . . . . . . . . . . . . . . . . . . . . . 126 Other Crops . . . . . . . . . . . . . . . . . . . . . . 129 Farmland Loss . . . . . . . . . . . . . . . . . . . . . 131 Bibliography . . . . . . . . . . . . . . . . . . . . . . 133 a=R 3 - INDUSTRIAL LAND USES Introduction . . . . . . . . . . . . . . . . . . . . . . 134 Industrial Land Use . . . . . . . . . . . . . . . . . . 134 The Mississippi River Parishes . . . . . . . . . . . . . 137 St. John the Baptist Parish . . . . . . . . . . . . . . 139 Oil and Gas Exploration And Support Facilities: The Coastal- Parishes . . . . . . . . . . 144 Bibliography . . . . . . . . . . . . . . . . . . . . . . 161 CHAPTER 4 - CONFLIM IN LAND USE Introduction . . . . . . . . . . . . . . . . . . . . . . . 162 Uses of the Land Versus the Environment . . . . . . . . . .163 Conflicts Between the Uses of Ilan . . . . . . . . . . . . .175 Wetlands . . . . . . . . . . . . . . . . . . . . . . . . . 184 Sumary . . . . . . . . . . . . . . . . . . . . . . . . . . 196 Bibliography . . . . . . . . . . . . . . . . . . . . . . . 198 LIST OF TABLES P.AIG I THE NATURAL SEITING TABLE 1. 1 Morgan City 1951-1973 . . . . . . . . . . . . . . . . . . 10 TABLE 1.2 Houma 1951-1973 . . . . . . . . . . . . . ... . . . . . . 11 TABLE 1. 3 Ca.rville 2 SW 1951-1973 . . . . . . . . . . . . . . . . . 12 TABLE 1. 4 Average Relative Humidy New Orleans, Louisiana . . . . . . 15 TABLE 1.5 Air Quality Monitoring Sites . . . . . . . . . . . . . . . 18 TABLE 1.6 Ambient Air Quality Standards . . . . . . . . . . . . . . 19 TABLE 1. 7 Suspended Particulate 1978 . . . . . . . . . . . . . . . . 20 TABLE 1.8 Nitrogen Dioxide Bubbler 1978 . . . . . . . . . . . . . . 21 TABLE 1.9 Sulfur Dioxide Bubbler 1978 . . . . . . . . . . . . . . . 22 TABLE 4.1 Soil Chart . . . . . . . . . . . . . . . . . . . . . . . . 54 TABLE 5. 1 Percentage of Tree Species in Cypress-Tupelo Gun Swan'p and Bottomland Hardwood Forest of the Barataria Basin . . . . . . . . . . . . . . . . . . . . . 60 TABLE 5.2 Percentage of Plant Species in Fresh Marsh Portions of Barataria Basin . . . . . . . . . . . . . . . 63 TABLE 5. 3 Percentage of Plant Species in Brackish Marsh Areas of Barataria Basin . . . . . . . . . . . . . 66 i TABLE 5.4 Percentage of Plant Species in the Saline Marsh Region of Barataria Basin . . . ... . . . . . . . . . . . . . . . 68 TABLE 5.5 Plant Species Conposition of Spoil Banks and Natural Levees in Coastal Louisiana . . . . . . . . . . . . 70 TABLE 6.1 Lake Pontchartrain Basin Stream Segment Description . . . . . . . . . . . . . . . . . . . . 78 TABLE 6.2 Terrebonne Basin Stream Segneent Description . . . . . . . . 82 TABLE 6.3 Terrebonne Basin Major Rivers . . . . . . . . . . . . . . . 83 TABLE 6.4 Terrebonne Basin Major Lakes . . . . . . . . . . . . . . . 84 TABLE 6.5 Parishes in Lower Mississippi Basin . . . . . . . . . . . . 91 TABLE 6.6 Mississippi River Drainage Basin: Major Tributaries . . . 91 TABLE 6.7 Punpage of Water in South Central Louisiana by Parish, Source, and Principal Use, 1975 . . . . . . . . 94 TABLE 7.1 Physical Properties Governing Productivity of Estuarine System TABLE 7.2 Ecological Roles of Sow Estuarine Species 103 TABLE 7.3 U. S. Comercial Landings . ... . . . . . . . . . . . . . . 104 TABLE 7.4 U. S. Conm-@--rcial Landings . . . . . . . . . . . . . . . . . 108 TABLE 7. 5 Benefits of the Estuarine Ecosystem . . . . . . . . . . . . 109 ii PART II - LAND USE TABLE 1 * 1 Total Population . . . . . . . . . . . . . . . . . . . . . 121 TABLE 1.2 White Population . . . . . . . . . . . . . . . . . . . . . 122 TABLE 1.3 Black Population . . . . . . . . . . . . . . . . . . . . . 123 TABLE 2. 1 Major Crops in the South Central Region . . . . . . . . . . 130 TABLE 2.2 Total Cropland . . . . . . . . . . . . . . . . . . . . . . 132 TABLE 3. 1 Recent History of Industrial Investment by Parish for East South Central Louisiana . . . . . . . . . . . . . 135 TABLE 3.2 Existing Industry . . . . . . . . . . . . . . . . . . . . . 141 TABLE 3.3 St. John the Baptist Parish Proposed Industry . . . . . . . 142 TABLE 3.4 St. John the Baptist Parish Employment By Industry, 1978 . . . . . . . . . . . . . . . . . . . . . 143 TABLE 3.5 Manufacturers in Lafourche Parish (1972) . . . . . . . . . 146 TABLE 3.6 LandTarks of Resource Development in Lafourche Parish . . . 148 TABLE 3.7 Landmarks of Resource Development in Lafourche Parish. 150 TABLE 3.8 Landmarks of Resource Development in Lafourche Parish. . . 151 TABLE 3.9 Employment in Oil and Gas Related Primary and Secondary Industries in Lafourche Parish . . . . . . . . . . . . . . 152 TABLE 3.10 Percent of Offshore oil and Gas Production in the Houma District . . . . . . . . . . . . . . . . . . . 157 iii TABLE 3.11 Eaployment in Seafood Industries in Lafourche Parish for 1975-1976 By Quarter . . . . . . . . . . . . . . . . . . 158 TABLE 3. 12 Canwrcial Seafood Landings for Golden Meadow-Leevile Port . 159 TABLE 4.1 Major Reclamation Projects in the South Central District to 1961 . . . . . . . . . . . . . . . . . . . . . 170 TABLE 4. 2 Surface Area of Natural and @kumiade Water Bodies 1931-1942) 1948-1967, and 1970 . . . . . . . . . . . . . . . 173 TABLE 4.3 Highways Crossing Wetlands Areas in the South Central Central District . . . . . . . . . . . . . . . . . . 176 TABLE 4.4 Sanitary Landfill Sites . . . . . . . . . . . . . . . . . . 180 TABLE 4.5 Sewerage Disposal Methods SCP&DC District . . . . . . . . . . 183 TABLE 4.6. Fish and Shellfish Landings and Value for Louisiana . . . . . 186 TABLE 4. 7 Percentage of Trapping Harvest From Louisiana Wetlands . . . 187 TABLE 4.8 Average Annual Harvest of Pelts From Louisiana Wetlands (By Species) 1970-1971 ThroLgh 1974-1975 . . . . . . 188 TABLE 4. 9 Annual Harvest of Pelts in Louisiana (All Species) 1967-1968 Through 1975-1976 TABLE 4.10 Average Annual Pounds of Meats From Louisiana Wetlands (By Species) 1970-1971 Through 1974-1975 . . . . . . . . . . 190 TABLE 4. 11 Annual Harvest of Meats From Furbearing Animals In Louisiana (All Species) 1967-1968 Through 1976-1977 . . . . . 191 TABLE 4. 12 Estimated Gross Economic Contribution ofa Wetland Acre in the Barataria Basin . . . . . . . . . . . . . . . . . . 192 TABLE 4.13 Estimated Net Economic Contribution of a Wetland Acre in the Baxataria Basin . . . . . . . . . . . . . . . . . . 193 TABLE 4..14 Revised Estimate of Gross Economic Contribution of a Wetland Acre in the Barataria Basin Based on U. S. Army Corps of Engineers Regulations . . . . . . . . . . . . 194 v LIST OF FIGURES PART I - THE NATURAL =ING FIGURE 1. 1 Solar Radiation Budget . . . . . . . . . . . . . . . . . . . 5 FIGURE 1.2 Average Yearly Ten-perature . . . . . . . . . . . . . . . . . 7 FIGURE 1.3 Average Yearly Precipitation . . . . . . . . . . . . . . . 14 FIGURE 2. 1 Geologic Tim Scale . . . . . . . . . . . . . . . . . . . . 25 FIGURE 2.2 Louisiana Physiographi Regions . . . . . . . . . . . . . . 26 FIGURE 2.3 Gulf Coast Geosyncline . . . . . . . . . . . . . . . . . . 27 FIGURE 2.4 Salt Dome Geologic Structure . . . . . . . . . . . . . . . 28 FIGURE 2.5 Salt Dom Map . ... . . . . . . . . . . . . . . . . . . . . 29 FiGURE 2.6 Cross Section of a Salt Dome . . . . . . . . . . . . . . . 31 FIGURE 2.7 Fault Map . . . . . . . . . . . . . . . . . . . . . . . . . 33 FIGURE 3.1 Deltas of the Mississippi . . . . . . . . . . . . . . . . . 36 FIGURE 3.2 Approximate Position of the Shoreline During Maxinm Gulf of Mexico Transgression . . . . . . . . . ... 38 FIGURE 3.3 Ice Age Louisiana Shoreline Greatest Seaward Advance . . . 39 FIGURE 3.4 Identification Map for Delta Lobes of the Mississippi . . . 41 vi FIGURE 3.5 Tim Sequence for Mississippi Delta Lobes . . . . . . . . . 42 FIGURE 3.6 1@ Life Cycle Cross Section of a Deltaic Plain . . . . . . . . 48 FIGURE 3.7 Geomorphological Features . . . . . . . . . . . . . . . . . 49 FIGURE 4. 1 Soils of South Louisiana . . . . . . . . . . . . . . . . . 55 FIGURE 5.1 Vegetation of South Louisiana . . . . . . . . . . . . . . . 72 FIGURE 6. 1 Drainage Basins . . . . . . . . . . . . . . . . . . . . . . 76 PART II - LAND USE FIGURE 3.1 Manufacturing Shipments and Plants in East South Central Louisiana, 1977 . ... . . . . . . . . . . . ... . . 136 FIGURE 3.2 Manufacturing Locations and Employment Levels in East South Central Louisiana . . . . . . . . . . . . . . 138 FIGURE 4. 1 Project Design Capacity: Mississippi River . . . . . . . . 166 FIGURE 4.2 Land Loss Acres Per Year . . . . . . . . . . . . . . . . . 174 vii DISTRICT LOCATION IN THE STATE CITY LOCATIONS IN THE DISTRICT Gramercv Lutcher STJOHN HE BAPTIS ST JAM Naooleonvill Assuh;.PTIO ST. CHARU Tlvbodaux Lockport Hou m a LAFOURCHE TERSESONNE Golden Meado INMDUMON The production of this se ries of reports under the HUD 701 Program has been needed in our area for quite some time. Nu-nerous documents, research papers, books, maps, etc., exist providing detailed descriptions of the physical components of the South Central Area. However, there is currently no one source available to present a complete overview of the region without becoming embroiled in the minute details of the physical parameters discussed in this document. This report is therefore an attempt to collect and present such data in a single document for use by the many clients served by South Central Planning. The Report Series is divided into three phases: (1980-81) 1. Description of Land Cover (Geology, Climate, etc./ Land Use) in the South Central Region (1981-82) 2. Cor@arison of Land Use Changes from the 1973 Iand Use and Data Analysis (LUDA) land use study to the 1980 Land Areal Resource Information System (LARIS) land classification (1982-83) 3. Project Future Land Uses and Policies to deal with anticipated changes The phasing of this report was necessary due to the limited financial resources of the agency, the unavailability of essential land use data this year, and the lack of personnel to do the vork. 1980-81 REPORT: DESCRIPTION OF LAND ODVER The body of this year's report is divided into two sections. Part I - The Natural Setting: Chapter 1 - Climate Chapter 2 - Geology Chapter 3 - Geomrphology Chapter 4 - Soils Chapter 5 - Vegetation Chapter 6 - Drainage and Groundwater Chapter 7 - The Wetlands Ecosystem Part II - Land Use: Chapter 1 - Population/Settlement Patterns Chapter 2 - Agriculture Chapter 3 - Industrial Land Uses Chapter 4 - Conflicts in Land Use The above topics cover the main parameters of importance within our region regarding land use. Special chapters on the Wetlands Ecosystem and the Oil and Gas Industry were also added, due to the tremendous importance these areas have for the region as well as the entire country. CONCLUSION We feel that the elements included in this year's report will provide several inportant services to the user. 1. Provide a general information base about the region. 2. Provide a bibliographical source list if wre detailed inform- tion is needed by the user. 3. Fill a gap in infonmtion availability for our agency. 4. Serve as a base for the many grant applications and requests that utilize this kind of data. 2 5. Provide a resource document for local officials to use in the planning process. Although this report uses technical terms and descriptions, we have attempted to compron-Lise the two considerations of easy readability and technical information so as to reach the greatest range of people with the information contained herein. Finally, we intend to update this and subsequent reports to keep the information current and usable to all who request it. This report will be made available to local governmental entities for their use. We hope that you, the reader, find this docunent interesting, informative, and capable of meeting your planning needs. Director of Plantfing 3 PA RT I THE NATURAL SETTING CHAPrER 1 - CLIMATE By Edwin J. Durabb INTRODUCTION The climate of the South Central District has been categorized by the Koppen-Geiger system of climatic classification as a "Cfa" type climate, i.e. warm and moist with a warm summer (Muller and Oberlander, 1978). One reason for the moisture and heat that dominates our climate is the Gulf of Mexico. This body of water provides the heat and moisture supply for the entire eastern half of the United States for significant portions of the year. The land area of our planning district sits immediately adjacent to this moisture source. Water temperatures in the Gulf, off the Louisiana coast, range from a low of 64OF in February to 849F in July (U.S. Department of Commerce, 1979). This accounts for the moderating influence of Gulf air in the winter and hot, humid air in the straner. Another main factor in our climate is our subtropical latitude. Although the geomorphology and climatic patterns of the United States and Canada allow colder continental air to intrude into the region on occasion, our subtropical latitude moderates the effect of these incursions in the winter. We receive high levels of solar radiation and actually receive more solar radiation than we lose to space for nearly eleven months out of the year (see Figure 1.1). Thus, the main components that shape our climate are latitude and proximity to the Gulf of Mexico. The following is a brief sumnary description of the parameters that make up the climate of the South Central Region. 4 FIGURE 1. 1 SOLAR RADIATION BUDGET 600 Outgoing terrestrial radiation to space 500 Gain 0 7 400 - Deficit CL 300 200 4-- Incoming solar :3 CL radiation absorbed 100 w 0. 1 A (y 10* 200 300 4e 5 do 6d* 700 900 SCPaDC LOCAT 10 N 1AL a-t tude (ON) SOURCE: Muller Ek Oberlander 1979 - pg 71 TBUYERATUIRE Yearly average temperatures for the region reflect the subtropical latitude of the area, (see Figure 1.2). The area is categorized by long, hot summers and short, cool spring, fall and winter periods. Temperatures are uniformly hot with a high humidity in the summers. Highest temperatures generally occur in the inland areas. Spring, fall and winter generally consist of moderately warm humid periods dcminated by tropical Gulf air, broken occasionally by Pacific or Polar continental drier-cooler air masses. The polar air incursions occur most often in the winter and can bring large sudden drops in temperature. In the winter, as in the summer, the coldest local temperatures occur inland and away from wetlands and water bodies. Extreme temperatures for the district range from 11OF at Carville in the north in January, to lW'F at the same station in August. (See Table 1.1, 1.2, 1.3 for detailed temperature observations from three selected st ations. The growing season in the southern part of Louisiana is extremely long averaging over three-hundred days in the northern part of the district and nearly three-hundred, sixty-five days near the coast. Occasionally, an early frost or freeze can damage the agricultural interests in the district since the main crop of sugarcane is a tropical plant susceptible to freeze damage. However, the average number of days when the minimum temperature drops below 32OF is only seventeen at Carville, fifteen at Houma, and thirteen at New Orleans. Rarely do temperatures drop below 209F anywhere in the district. 1Note that there are no recording weather stations in the northern part of our district. Therefore, we have chosen the closest station avail- able outside of the district boundary which is Carville, Louisiana. 6 FIGURE 1.2 M s s I s p p L% V.- 6 66.9* 67 67.4* %7:Z am. " 0= 67.4* 67.4* L AKE Boy St 67.7 68.01 LAKE PWMAIN 4W ri q rA.6' Pd,.d,. F ... kli. . 69 LAKE A SAL.0 9.3 if r,.73, S0,00 % 00 L@? soam...l. k2l P AVERAGE YEARLY TEMPERATURE S"CE Map by tf@ompil d by Wthor from worm. so-es DISTRICT BOUNDRY provided U.S. Department of Comm.rc* Scal. 1 500,000 Notio".1 OCGGnic & Atmoi,pheric Administraflam Oalialcol *.-rias.scpam crofti"O...- WTE Tid. -p iS K@mf f. ilWOr.tiom pl-.i.9 P.P.0s Wly. ---------- - - --------- ---- There are several factors that periodically effect the local climate picture. These are: 1. Proximity to the Gulf of Mexico. 2. Proximity to wetland areas and inland waters. 3. Proximity to the Mississippi River. 4. Urban influences. . Proximity to the Gulf of Mexico Proximity to the Gulf of Mexico accounts for a significant increase in yearly temperature. More iniportantly, the impact of occasional surges of cold polar continental air is moderated by both wetlands and the Gulf itself thus altering temperatures. Water stores large quantities of heat and releases it slowly over time. This accounts for the fact that water takes longer to warm up and cool down in relation to the land surface. This fact causes a reduction in the temperature range over water and the adjacent land-masses. This is reflected in the fact that Black Mangrove, a tropical type plant intolerant to freezes or even frost, is found inmediately along the coast. Although there are no reporting weather stations on the coast in our distri-@t, the existence of Black Mangrove suggests a mre n-oderate climate than in the interior where temperature occasionally drops below 320F in the winter. Proximity to Wetland Areas and Inland Waters Temperature differences between water and land account for the sea and land breezes that moderate temperatures along the coast. Louisiana, with its vast inland marshes, swamps, bays and lakes, allows this nx)der- ating effect of water to extend far inland. Sea and land breezes can 8 occur along lakes, for example, Lake Pontchartrain in the north of the region, and the water moderates temperatures wherever it is located. Since eighty-two percent of our district has water cover for most of the year, the influence in climate is significant (South Central Planning & Development Commission: 1976:1.) Proximity to the Mississippi River Since the Mississippi River is a large volune stream, local temper- ature irregularities are sometimes felt due to temperature differences between the water and the land. Whereas the Gulf of Mexico and local lakes are usually warm, the river water is cold, especially in the spring, causing localized fog and colder temperatures near to the channel. Urban Influences The predominantly rural South Central Planning and Development District only has three significant areas of man-made influences that alter temperatures. The cities of Thibodaux and Houna are large enough to generate heat and change the local micro-climate. The large industrial complexes along the River also produce enough heat to locally radse temperatures significantly. The following tables (Table 1.1, 1.2, 1.3) list climate sumaries for three communities that possess complete data collection capacity in or near our region. (Refer to Figure 1.2 for an overview of district temperature differences.) 9 TABLE 1. 1 h1WAN CI7Y 1951-1973 LXf 290 041' N 1DA3 91 111 W TI-WERAIURE (or) P11M.IPITATION TCFfALS (inchels) Means a traw- s Mean Greatest Monthly Year Month Naxl,,= Monthly Record Year I Day lRecord Year Mean I Itigh LOW I Jan. 64.3 43.6 53.9 84 1957 31st 12 1962 lIth 4.14 10.64 1966 .0 Feb. 66.6 45.5 56.1 86+ 1957 5th 17 1951 3rd 4.89 11.22 1966 .1 Mardi 72.2 51.4 6i.@ 88 1955 16th 28+ 19GB Ist 3.61 9.41 1973 .0 Apri 1 80.0 59.5 69.8 92 1955 30th 39 1953 19th 4.53 15.30 1973 .0 hly 85.7 65.3 75.5 96 1953 28th 45 1960 l3th 4.46 10.30 1969 .0 June 90. 6 70.9 80.8 101 1954 30th 55 1956 3rd 4.99 15.82 1963 .0 0 JU ly 91.8 72.9 82.4 99 1973 21st 60 1970 4th 7.90 20.34 1964 .0 Aug. 91.6 72.5 82.1 100 1962 12th 56 1956 23rd 6.65 10.05 19(30 .0 Sept. 88.9 69.4 79.2 99 1970 l3th 46 1967 30th 6.G4 18.00 1973 .0 'Out. 82.0 59.3 70.7 94 1954 4th .34 1952 30th 3.98 9.75 1959 .0 W,)V. 72.6 50.2 61.4 91 1973 5-th 28+ 1959 l8th 3.61 11.65 1963 .0 Dec. 66.7 45.5 56.2 84 1.951 7th 12 1962 13th 5.44 11.80 19G3 .0 YrAt 7-3.4 53.8 69.2 101 19fA June 1:2) + 1962 Dec. 60.84 20.34 July .1 30th 13th 1964 + Also recorded on earller dates. SDURCE: U.S. Morgan City Supplemental Data Mean Number of days Maximum 90 0 and above: 94 days Mean Number of days Minimum 32 0 and below: 12 days Greatest Daily Precipitation: 7.17" - June 17, 1963 TATIE, 1. 2 IICUMA IA,r 290 35' A 1951-1973 WAG 900 44' W Elevation 15 feet 'III&MIUM. (or, PRBCIPITNrION WrAIB (indies) Means Dctruws Mein Greatest Mont1ily Year Snow, Sleet I,= Monti, ly Record Makimul" Ilontkily Year Itigh low I Month Maximn Min Year I Day Record 177_t Jan. 65.0 44.5 54.8 83 1952 2nd 12 1962 11th 4.58 12.36 196G .0 .0 reb. 67.3 46.3 56.8 85 1957 4th 13 1951 3rd 4.8G 10.28 1966 .1 2.5 1958 March 72.7 52.0 62.4 88 1965 25th 28+ 1968 1st 4.13 9.50 1973 .0 .0 April 79.8 59.6 69.7 90+ 1965 13th 34 1971 8th 4.37 14.06 1973 .0 .0 I&I'y 85.3 65.1 75.3 96 1953 28th 44 1952 12th 4.78 15.44 1959 .0 .0 Julie 90.1 70.3 80.2 99 1954 30th 55 1966 2nd 6.45 14.08 1963 .0 .0 Ju ly 90.9 72.5 81.7 99 1960 22nd 59 1967 16th 8.09 18.85 1-954 .0 .0 Aug. 90.7 72.2 81.5 100 1951 15th 60 1967 12Lh 6.51 10.55 1960 .0 .0 Sept. 87.7 69.2 78.5 98 1964 1st 44 1967 30th 8.05 19.41 1973 .0 .0 CICL. 81.5 58.6 70.0 94 3.962 9th 31 1952 30th 3.10 11.60 1659 .0 .0 I\bv. 72.8 50.5 61.7 87+ 1956 2nd 25 1951 18th 3.20 13.26 1963 .0 .0 00c. 67.5 46.2 56.9 84+ 1956 7 th 15 1-962 l3th 5.17 11.56 1967 .0 .0 YEAR 79.3 58.9 69.1 100 Aug. 12th 12 Jan. Ilth 63.59 19.41 Sept .1 .0 1951 1962 1973 + Also on earlier dates SOUfff,: U.S. Department of Comwrce, 1975. Houma Supplemental Data Mean Number of days Maximum 90 0 and above: 83 days@ Mean Number of days Minimum 32 0 and below: 15 days Greatest Daily Precipitation: 11.35" - May 31, 1959 TABLE 1. 3 CARVILI-E. 2 SW 1951-1973 Elevation 26 feet LAT 3(P 12' N LoiqG 910 071 W '11-MIERAIMIE (Or) PRECIPITATION WrALS (inches) Means n(tremes Mean Greatest Monully Year Snow, Sleet Wily Record ar Day Ifean K-L,l,um Mini. ;;@@Ot Day .!@@dte--qr P"iman blontlijy ear jan 63.1 41.6 52.3 82 1957 31st 11 1962 11th 4.30 10.65 1966 less 1.0 1973 than reb. 65.7 43.5 54.6 84 1.957 4 th 13 1951 2nd 5.39 14.36 19G6 1 2.0 1973 6hrdi 71.9 49.2 60.6 88 1967 15th 24 1968 Is t 4.20 9.32 1972 .0 .0 April 79.5 57.2 68.4 91 1955 30th 35 1971 801 4.32 11.22 1969 .0 .0 May 85.7 63.9 74.8 96-1. 1953 28th 43 1970 4 Lh 4.96 11.21 1959 .0 .0 June 90.9 69.8 80.3 100 1954 30LIt 55 1952 Ist 4.13 10.91 1957 .0 .0 July 91.7 72.3 82.0 100 1960 22nd 58 1967 15th 6.70 12.52 1959 .0 .0 Aug. 91.5 71.8 81.7 102 1962 l0Lh 60 1,956. 23rd 5.61 1-1.24 1960 .0 .0 Sept. 88.4 68.4 78.4 97+ 1963 4Lh 45 1967 30th 5.28 15.58 1973 .0 .0 Oct. 81-1 58.0 69.6 93+ 1962 13th 34 1957 28 Lit 2.66 9.51 1.964 .0 .0 Nov. 71.2 .19.0 60.2 87 l9r7l 2nd 25+ 1970 24 th 3.86 8.36 1957 .0 .0 Dec. 65.1 44.1 54.6 92 1971 31st 13 1962 13LIi 6.22 14.48 1971 .0 .0 YEAR 73. 8 57.4 68.1 102 Aug. 10th 11 Jan. 11th 57.63 15.58 Sept. .1 .0 1962 1962 1973 SOURCE: U.S. Department of C"merce, 1975. + Also recorded cm earlier (hites. Carville Supplemental Data 0 mean Number of days Maximum 90 0 and above: 90 days mean Number of days Minimum 32 and below: 17 days Greatest Daily Precipitation: 5.85" - December 10, 1961 PRECIPITATION Precipitation in the district is heavy throughout the year. There are, however, t%o wet periods and one drier season. The two wet seasons occur in July-August, and Deceirber, respectively. The drier period extends from late Septenber to mid-Novenber (U.S. Department of Conmrce, 1979). Rainfall in the sum)er is usually associated with tropical air mass afternoon convection thunderstorms. Precipitation is heavy but of short duration. Rainfall in the winter is usually associated with cold frontal passages and, occasionally, low- pressure areas in the Gulf of Mexico. This rainfall is moderate and more widespread in nature. Sometimes heavy rains are associated with tropical waves or stomis in the late sumner and fall. Fran 1954-1976, nine tropical storms or hurricanes passed through or near enough to the district to effect local precipitation (U.S. Department of Interior, 1977). Snow and sleet are extremely rare inland and almost non-existent along the coast. For example, measurable snow has occurred only once in Houma during the period of 1951-73 and twice in Carville, Louisiana. Figure 1.3 illustrates that maxinum yearly precipitation occurs soniewhat inland from the coast line. This is probably due to the warn-dng effect of the land as mist ocean air passes over it. The large expanse of coastal marsh make the transition from a water to land base extremely .Slow. Relative hunidity, the component of the local climate that makes our weather most uncomfortable, is high throughout the year. Table 1.4 illustrates the yearly mans of Relative Humidity for New Orleans. The driest and wettest monthly averages are also included. 13 FIGURE 1.3 M S S i S I p p I L ON. 61.28* 60.44" 63.00* 62" 6 .56 ZG@225V lbolon 54.. is in -0 56 58 LAKE 57-241' MAUM LAKC PWCHOrRAIN ej '41 % to 60.20" rift 06 a 'j 63.4d" S@ 62.81' ,onkiln SA LAKE 4MMM-000"', 4 64" 65.7? % 4* 0 10 000 W.' 62 % Q) 'ell 57-59' LIT AVERAGE YEARLY PRECIPITATION Map conWilled by wittior firime. micks sulac P. R by the U. S. Departmentl of Conscience Naikx at Oceanic & Atmoophoic Adininislivilon DISTRICT BOUNDRY Scale 1- 500.000 statistical woommarkims. SCPaW Omhiq Depmri@. 110TE-Thiso nff Is meant for ill-tatlon planning v. porticoes on Y. TABLE 1. 4 AVERAGE RELATIVE HUM1DI`IY NEW ORLEANS, LDUISIANA Midnight 6:00 A.M. Noon 6:00 P.M. (Dry) March 83 % 85 % 61 % 65 % (Dry) November 84 % 86 % 60 % 74 % (Wet) July 89 % 91 % 66 % 73 % YEARLY AVERAGE 85 % 88 63 71 % SOURCE: U. S. Departmnt of Comwrce, 1979. 15 WINDS Prevailing winds generally blow from a southerly direction for about half the year. In the late fall, winter and early spring, intru- sions of continental air into the region cause the resulting direction to shift primarily to a northeast or northerly component. Winds are generally light in the sumier with maximum speeds associ- ated with the brief localized down drafts of afternoon thunderstoms. Winds can occasionally be much stronger in the late sumier and fall due to tropical storm or hurricane activity. For example, along the coast at Grand-Isle, estimated peak winds during Hurricane Betsy exceeded 120 MPH. This extreme wind is rare and always localized to coastal regions. In the winter, strong southerly winds or northerly winds associated with low pressure system and high pressure centers blow for brief periods. 2 Wind velocities are generally higher in the winter. At New Orleans average wind speed ranges from 6.1 MPH in August to 10.3 MPH in March. The average being 8.4 MPH (U. S. Department of Goniwrce, 1979). 2New Orleans was the closest available station with wind data. There are no stations within the SCP&DC district that keep this type of record. 16 AIR QUALITY Due to the recently developed heavy industries associated with the petro-chemical industry in the South Central District, and in response to the National Clean Air Act, Louisiana has-established an air quality mnitoring and control Program. Table 1.5 lists the air quality monitoring stations in and near the South Central Region. Table 1.6 lists the air quality standards currently being used in Louisiana to mnitor pollutants. Figures 1.7, 1.8 and 1.9 represent air quality monitor records (for five selected status) for the year 1978 to provide a reference point to determine the air quality in the SCP&DC district. 17 TABLE 1. 5 AIR QUALITY MONITORING SIIES CITY S ITE NAME ADDRESS PARISH Carville USPHA Hospital Highway 75 Iberville Donaldsonville Riverdale Subdivision Highway 18 Ascension Garyville Mobile Trailer Lot Azaleas, Apricot St. St. John Geismar Wintz Mart Market Highway 75 Ascension Harvey West Jefferson P.H.U. 1901 8th St. Jefferson Metairie Borden Company 1751 Airline Hwy. Jefferson Metairie East Jefferson P.H.U. 111 N. Causeway Blvd. Jefferson SOURCE: Louisiana Air Control Commission, 1978: p. 3, 4. MONITORING PAFLAA1ETERS Continuous Non-Continuous 03 SO2 TSP S02 N02 Carville X X X X Garyville X X X X Geismar X X X Harvey X X X Metairie Donaldsonville 02 = Ozone S02 = Sulphur Dioxide N02 = Nitrogen Dioxide TSP = Total Suspended Particulates 18 TABLE 1. 6 AMBIENT AIR QUALITY STANDARDS (Non-continuous Data) MAXIMUM ANNUAL ANNUAL CONVERSION FACTORS PARAMETER 24 hour average GEOMETRIC ARITHMETIC (25*C 760mm Hq) MEAN MEAN Total Prim. 260 ug/m3 75 ug/m3 Suspended Particulate Sec. 150 ug/m3 60uglm3 365 ug/m3 80 ug/m 3 Sulf ur Prim. (0.14 ppm) (0.03ppm) 3 Dioxide 3 3 ppmx2620=ug1m 260 ugim 60 ug1m Sec. (0.10 PPM) (0.02 ppm) 100 ugim3 Nitrogen Prim. 1015 ppm) 3 Dioxide 10ougIM3 F,Prn x 1880 ugim Sec. (0.05 ppm) 1.50COH/1000 0-60COH0000 0.75COH11000 Soiling Prim. linear ft. linear ft. linear ft. Index Sec. SOLTEE: Louisiana Air Control Con-mission (1978), page 32. 01 N N (A (A 0 0 0 0 0 0 01 0 0 0 0 0 0 CARVILLE cn USPHS HOSPITAL GARYVILLE TRAILER GEISMAR WINTZ MEAT MARKET* HARVEY WEST JEFFERSON PH.U LN) po M E TA I R I E . ...... BORDENS COMPANY x z 01 (A 0 0 0 0 01 0 (31 0 0 0 0 0 0 ca CARVILLE USPHS HOSPITAL GARYVILLE TRAILER GEISMAR En WINTZ MEAT MARKET HARVEY WEST JEFFERSON PH-U METAIR I E BORDENS COMPANY 01 ()j Qj 0 0 0 0 c" 0 01 0 0 0 0 CARVILLE USPHS HOSPITAL GARYVILLE TRAILER GEISMAR WINTZ MEAT MARKET HARVEY WEST JEFFERSON PH-U 00 META I R I E BORDENS COMPANY m > z BIELIOGRAPHY Louisiana Air Control Commission (1979) Ambient Air Data Annual Report, 1978. Department of Health and Human Resources. U. S. Department of Commerce National Oceanic and Atmospheric Administration (1979) Climatological Data: Annual Summary Louisiana, 1978, Vol. 83, No. 13. U. S. Department of Cayrwrce, Environmental Data and Information Service, National Climatic Center, Ashville, North Carolina. Muller, R. A., and Oberlander, T. M. (1978) Physical Geography rfbday: A Portrait of a Planet. Random House, New York, New York. U. S. Department of Commerce National Oceanic and Atmospheric Administration (1975) Climatology of the United States No. 20: -Climate of Carville.2 SW Louisiana. U. S. Department of Commerce, Environmental Data and Information Service, National Climatic Center, Ashville, North Carolina. U. S. Department of Commerce National Oceanic and Atmospheric Administration (1975) Climatology of the United States No. 20: Climate of Houma, Louisiana. U. S. Department of Commerce, Environmental Data and Information Service, National Climatic Center, Ashville, North Carolina. U. S. Department of Commerce National Oceanic and Atmospheric Administration (1975) Climatology of the United States No. 20: Climate of Morgan City, Louisiana. U. S. Department of Commerce, Environmental Data and Information Service,National Climatic Center, Ashville, North Carolina. U. S. Department of Commerce National Oceanic and Atmospheric Administration (1979) Local Climatological Data: Annual Summary with Comparative Data: 1978. New Orleans, Louisiana. U. S. Department of Interior, Bureau of Land Management (No Date) Tropical Cyclone In The Gulf of Mexico and Atlantic Ocean 1954- 1976. New Orleans Outer Continental Shelf Office, Bureau of Land Management. U. S. Department of The Interior, U. S. Government Printing Office, Washington, D. C. 23 CHAPTER 2 - GBOLOGY By Irwin Fingerman INTRCDUCTION The South Central Region lies within a geologic basin which has been collecting sedirwnt since the Mesozoic Period (see Figure 2.1 for a geologic tirm scale). The depth of this sediment to crustal rock is estimated to be in excess of 60,000 feet. Fluctuations in sea level, over time, have caused these sediments to consist mainly of sand, gravel, clay, shale and linie-stone, during their sequential deposition. During the Cretaceous and Tertiary Period, carbonate coral reefs were distributed in the northern portions of St. John the Baptist, St. Charles and St. Jams Parishes, and a layer of salt was deposited during the Jurassic Period. The sinking of the Gulf Coast Geosyncline (a belt shaped basin area that subsides deeply) is a continuous process. The basin has down- warped, partially from the weight of the sedimnt load it has collected and partially from the conpaction of the sedimnt itself. This process has gone on for over 200,000,000 years. Recently, the downwarping has led to subsidence of surface features and to uplifting of the Pleistocene terraces to the north (Figures 2.2 and 2.3). These features are currently extant today in the Florida Parishes of Louisiana and in the South Central District area. 24 FIGURE 2A GEOLOGIC TIME SCALE DURA710N IN MnLICNS OF MILLIONS OF YEARS-AM YEARS ERA PERIOD EPOCH (approx. ) (approx. IMPORTAW BIOLOGICAL EVENns Recent began 10,000 years ago Quaternary RF-n-nt Pleistocene 2.5-3 2.5-3 CDMOIC - Pliocene 13-15 First am Miocene 12 First manlike primates Tertiary Oligocene 11 First apes Eocene 22 Grass spreads widely Paleocene 68 5m-7 -First elephants First horses Extinction of dinosaurs, giant marine reptiles, Cretaceous 72 flying reptiles, and ammonites First primates Angiosperms spread widely kx=IC- 140 First snakes Jurassic 65 First sequoias First birds 205 First turtles and lizards Triassic 25 First dinos-, and m=mals L 230 Last giant amphibians Permian 55 Extinction of trilobites, fusulinids, many corals, crinoids, and other inver-cebrates 285 First mmmLl-like reptiles Pennsylvanian 40 First conifers, ferns, and ginkgoes, first reptiles ..325 First flying insects First fusulinids Mississippian 25 Extinction of graptolites 350 Fi t seed plants First land-living vertebrates Devonian 60 First sharks First forests and insects 410 First ammonites PAI=OIC- Silurian 430 20 First land vegetation and air-breatting aai"ni Ordovician 70 First bone bearing animals First corals and bryozoans 500 First cephalopods First pelecypods First oonodonts Cambrian 100 First graptolites First gastropods Appearance of many invertebrate phyla: arthropods, L 600 mollusks, sponges, and echinoderms Upper --Uthough many local subdivisions are PREC.IMBRIAN Middle recognized, no worldwide system of naming has been evolved. The Precambrian lasted Lower for at least 3.5 billion years. Until more is learned, this lengthy interval may be divided into Lower, Middle, and Upper without fornal names SOURCE'. STOKES(1973): p9.122-123 25 FIGURE 2.2 LOUISIANA PHYSIOGRAPHIC REGIONS Uplands 0 I st c emn eI . . . . . . . . Pei T Alluvial V y al le Deltaic Plaim, Deltaic Plain SOURCE: MORGAN (1977) 26 FIGURE 2.3 GULF COAST GEOSYNCLINE $--Zone of Subsidence q Zone of UPI ift Uplifted Terraces Deltaic Plal Soo Level Flood Plain Recent Demic Deposits 74vom queftce's ......... Subcrustal Flow SOURCE- MORGAN (1977) FIGURE 2.4 SALT DOME GEOLOGIC STRUCTURE f'Y.: GAS 00 WATER ROLLOVER C@p RdCK ANTICLINE SALT OOME FAULT (OVERHANG) (-7GOUGE 17 30URCE: TEXACO (1979) FIGURE 2.5 SALT DOMES OF SOUTHEAST LOUISIANA 3 LAKE 0 AUREPA LAKE 4 PONTCHARTRAIN 9 ,0000000 13L KE ORGNE 12 17 14 16 LAKE SALV OR 19 21 BRETON SOUND 20 23 24 26 25 28 30 32 35 36 J1 38 AQ 0 " 1 0 37 0 47 48 46 40 43 i P 41 4 OT i 44 5 0 ',@ 0 0 50 52 0 51 53 @ALTWNIIE-.URFACE 10 REFERENCE NUMBER NOTA-r10IN OF ACCURACY* SOURCE: COMPILIED AND EDITED BY This Map IsTo Be Used For Planning .. E. LLACE. BASE MAP Pur MO Al DOMES A'.Poxes ONLY. Su-ey Mecamments DIFWlED(FROM LA. GEOLOGICAL OISITRICT BOUNDARY Not To Be Mo; Fr- This MAP SUFIV EY 1959) PARISH BOUNDARY SAIX DCKE IOCATER MART IBERVILLE PARISH PLAQUEMINES PARISH TERIUMONNE PARISH 1. Bayou Choctaw . . . . . 9S - 11E 13. Stella . . . . . . . . 14S - 23E 31. Bay Junop . . . . . . 21S - 14E 2. Bayou Bleu . . . . . . . 9S - 10E 24. Lake Hermitage . . . . 18S - 25E 32. Four Isle Dcme . . . . 21S - 16E 3. St. Gabriel . . . . . . 9S - .2E 27. Potash . . . . . . . . 18S - 15E 33. Dog Lake . . . . . . . 21S - 16E 4. White Castle . . . . . . IIS - 12E 28. Quarantine Bay . . . . 19S - 17E 34. Bay St. Elaine . . . . 22S - 18E 29. Lake Washington . . . . 20S - 26E 35. lake Barre . . . . . . 21S - 20E 38. Venice . . . . . . . . 22S - 30E 42. Lake Pelto . . . . . . 23S - 18E ASCENSION PARISH 39. Delta Duck Club . . . . 21S - 20E 43. Caillou Island . . . . 23S - 20E 5. Darrow . . . . . . . . . 10S - 2E 48. West Bay . . . . . . . 23S - 30E 6. Sorrento . . . . . . . . IOS - 4E 49. Garden Island Bay . . . 23S - 32E OFFS11DRE MAIN PASS AREA ST. MARTIN PARISH LAFaiRmE PARISH 30. BL. 46 7. Lake Mongoulois . . . . IOS - 9E 14. Chacahoula . . . . . . 15S - 15E 11. Lake Chicot . . . . . . 11S - 10E 15. Raceland . . . . . . . 15S - 19E GRAND ISLE AREA 21. Valentine . . . . . . . 17S - 20E 37. Bl, 18 23. Cut Off . . . . . . . . 18S - 21E 46. BL. 16 ASSUMPTION PARISH 25. Bully Carrp . . . . . . 18S - 20E 8. Napoleonville 12S - 13E 26. Clovelly . . . . . . . 18S - 22E SHIP SHOAL AREA 36. Leeville . . . . . . . 21S - 22E 40. BL. 32 44. Timbalier Bay . . . . . 23S - 21E 41. Coon Point (BLIK. 39) ST. JAMS PARISH 54. Bay de Chene . . . . . 19S - 24E 50. BL. 72 9. Hester-Vacherie . . . . 12S - 13E 53. BL. 113 JEFFERSON PARISH BAY MARCHARD AREA ST. CHARLES PARISH 19. Barataria . . . . . . . 16S - 23E 45. BL. 2 10. Good Hope . . . . . . . 12S - 8E 22. Lafitte . . . . . . . . 17S - 24E 12. Paradis . . . . . . . . 14S - 20E WEST DELTA AREA 16. Bayou dEsAllemands . . . 15S - 20E 47. BL. 30 17. Bayou Couba, . . . . . . 153 - 21E ST. &M PARISH 18. lake Salvador . . . . . 16S - 23E 20. Belle Isle . . . . . . 17S - 10E SOU711 PELM AREA 51. BL. 20 SOMI PASS AREA 52. ffL. 2-7 ECONOMIC AND MUCIURAL GEOLOGY Economically, the Gulf Coast geosyncline is very important. Deposits of natural gas, oil, sulphur and salt are numerous. 'Ihese natural re- sources have been found in the Miocene Age or younger strata. The South Central Region is one of the nation's leaders in oil and gas production. These deposits, to a large degree, depend upon a phenomena in the area known as salt dornes. Salt domes are intrusions of a Jurassic salt layer which, due to the enormous pressure subjected on the salt by overlying sediments and strata and to its ability to flow to areas of less pressure, are slowly rising toward the surface. This movement toward the surface includes breaking through the overlying strata or deforming it (Figure 2.4). Some of these domes of salt have risen as much as 40,00.0 feet from their original depth and several even have surface expressions of over 100 feet man sea level (m.s.l.). Db salt domes have reached the surface in the South Central District however. Figure 2.5 shows the locations of salt domes within the South Central Region. Oil and gas deposits are trapped by the piercement of strata by the salt dome. This allows the deposits to pool along the side of the salt. The deformation of the overlying strata also allows for pooling and trapping of oil and gas deposits (Figure 2.6). Sulphur, basite, gypsum, calcite and anhydrite are formed in a portion of the salt dome called the cap rock (Figure 2.6). Anhydrite precipitates out of groundwaters which come into contact with the salt, and the other minerals are formed by alteration of the anhydrite. The salt and sulphur can be mined. Examples of this inlcude Avery Island 30 FIGURE 2.6 CR03S SECTION OF A SALT DOME CALCITE DNE CAS04 TRANSITION ZONE BAS04 A HYDRI E Z Nj@, H M; 11h M SULPHUR SOURCE MORGAN (1977) 31 and Jefferson Island, Louisiana which are currently operating salt mines' on salt domes that have pierced the surface. Oil and gas are also trapped by pinchouts of sand layers and by faults. Faults are a disruption of the strata that change the general alignment of the strata. Salt domes usually have numerous faults above them. Sometimes, however, faults are caused by other means. The South Central Region is crossed by a series of fault systems which trend west to east (Figure 2. 7). These faults were brought on by the nature of the deposition of sediment causing weak sections of strata to give way or by salt layers applying pressure from below. Geologists are not certain what the origin of the fault system is. In most cases in the South Central District, these faults are buried by newer sedinjent and thus have no surface expression. SLWAARY The geology of the region is complex. Certain geologic processes are still continuing. The Gulf Coast Geosyncline continues to subside and salt domes are still rmving toward the surface. Surface expressions of recent geology will be discussed in Chapter 3, entitled Geomorphology. 32 FIGURE 2.7 FAULT MAP OF SOUTH LOUISIANA t 0 LAKE MAUREPAS LAKE PONTCHARTRAIN Y<9 C> PAX 14 BRETON 41 41 NOTATION OF ACCURACY' SOURCE: Compiled and Edited This map is to be used for planning W. E. WALLACE. Base Map M.1171ed Purposes only. Survey measurements am from La. G"ogical Survey.111959) -1-1 LAND FAULTS not to be made from this map. SCALE: MILES PIMSH BOUNDARY DISTINCT BOUNDARY- 5 3 1 0 10 15 20 25 L BEELIOGRAPHY Craig, N. J. et. al. (1979) "Land Loss in Coastal Louisiana (U.S.A.)", EnviromTie7-n-ta:l-Managerrient, Volume 3, NLurber 2. Halbouty, Michel T. (1967) Salt Dorries Gulf Region, United States and Mexico. Gulf Publishing Company, Houston, Texas. Morgan, Joel David (1977) Geoscience and Man, Volume XVI-The Mississippi River Delta - Legal Geomrphologic Evaluation of Historic Shoreline Changes. School of Geoscience, Louisiana State University, Baton Rouge, Louisiana. Murray, Grover E. (1961) Geology of the Atlantic and Gulf Coastal Province of North America. Harper & Brothers, New York, New York. Stokes, W. E. (1973) Essentials of Earth History. Prentice-Hall, Inc., Englewood Cliffs, New Jersey. Texaco (1979) Diagramatic Geologic Cross-Section Louisiana Gulf of Mexico Salt Dome Basin. Texaco, Inc. 34 CHAPTER 3 - CBOMORPHOLOGY By Edwin J. Durabb INTRODUCTION The land area of the South Central District sits astride one of the most dynamic geomorphological systems in the United States, the Missis- sippi River Deltaic Plain. Prior to 6,000 years ago, the land axea now exposed in our district was part of the continental shelf of the Gulf Coast and largely under water. From that point to the present, the Mississippi River distributaxy system has created several delta lobes extending far out into what once was the Gulf of Mexico (Gagliano & Van Beek, 1970). Figure 3.1 illustrates the aerial extent of the main deltas formed by the river as it shifted its course in the coastal waters of Louisiana. As one can easily see, these deltaic land forms extended much further into the Gulf than their current land expressions indicate. Severe erosion has destroyed land areas no longer occupied by the main river channel. The dynamic cycle of delta building and erosion has thus created the unique landscape that has delineated the resource base and settlement patterns existing today in the district. The follow- ing sections explain the alluvial processes that have shaped our land- scape and the results of natural interactions on the system. 35 FIGURE 3.1 DELTAS OF THE MISSISSIPPI -4) ,:01 6- y A- T'C"' _f'@_/IILTA Cllltll ST. BIRNAND DELTA COMPLIX..." CA) A L mcl @DIILTA COMI Ft A OU IM IN it -MO D IRN - -'DELTA COMPLEX tit MAXINGO qj% u DELTA COM ILI, y, , :@, 11 ."Ice wtol SOURCE: GAGLIANO a VAN BEEK (1970) RECENT GEOLDGIC HISMRY The physical expression of the geology of Southern Louisiana can be classified into four areas; the Pleistocene terrace, the marginal del- taic plain, the deltaic plain and the alluvial valley. Northwestern Assunption Parish lies in the alluvial valley area, the remainder of the region lies within the deltaic plain. The alluvial valley area consists of sediment (alluvium) deposited within the Mississippi River Valley as it cut through the tertiary uplands and Pleistocene terraces (see Figure 2.1 for their relative ages). The deltaic plain area was originally under water. Approximately 18,000 to 20,000 years ago the sea level was lowered about 390 feet below current sea level. This was in response to conti- nental glaciation. `Ihe shoreline was relocated close to the outer margin of the continental shelf (Figure 3.2). The Mississippi River cut a trench into the resultant Pleistocene prairie terrace in an effort to adjust to the new sea level. This trench occurred west of the present course of the Mississippi, probably in the western portion of the South Central Region. 'Ihe sea level started to rise about 18,000 years ago. Stream began filling in their valleys in an attenpt to adjust to the rising sea level. About 6,000 years ago the rise.in the sea level slowed, but continued until it reached its current level. The Pleistocene prairie was inundated and the coastline relocated to what is now far inshore (Figure 3.3). It was at this point that the Mississippi River began to shape the landscape that currently exists in the South Central Region. 37 FIGURE 3.2 APPROXIMATE POSITION OF THE SHORELINE DURING MAXIMUM GULF OF MEXICO TRANSGRESSION a Floodplain Deposits ................ - - - - - - . ..... Sand Beaches Pleistocene Praire TerTace NEW ORLEANS HOUMA GULF F M Miles 3b SOURCE: MORGAN (1977) 38 FI G*U RE 3.3 ICE AGE LOUISIANA SHORELINE GREATEST SEAWARD ADVANCE PRESENT, C'OAST ICE AGE COAST SOURCE: MORGAN (1977) mmmmj 39 RECENT ALLUVIAL PROCESSES During the last 6,000 years after sea level adjusted itself to near its present level, the Mississippi River began discharging huge amounts of sediment onto the continental shelf. In the process of deposition, areas that were once sea bottom were elevated above the ocean as deltaic deposits accumulated. The River continually shifted course, always seeking a shorter path to the sea, thus abandoning one delta and creating a new one. During these manderings over the last 7,500 years, six delta complexes have been created by the River. These are: 1. Maringouin 7500-6200 years ago 2. Teche 5700-3900 years ago 3. St. Bernard 4700- 700 years ago 4. Lafourche 3500-Present 5. Plaquemines/modern 1000-Present Figures 3.4 and 3.5 illustrate the shifting courses of the Missis- sippi as it deposited sedimnt across the continental shelf in Louisiana. Of the major delta systems only the earliest (Maringouin) has no surface expression. Deltaic lobe systems that have created the land of the South Central Region include the Teche, Lafourche and St. Berna-rd systems. Because these deltas were formed at different times and loca- tions, they axe in various stages of development a@s landforms. The deltaic depositional distributory system created discrete land- form systems in the South Central Region. These are: 1. Natural Levees (Depositional Landform) 2. Inter-Distributary Basins (Depositional-Subsidence Landform) 3. Barrier Island/Beach Ridges (Erosional Landfo:rm) 40 FIGURE 3.4 IDENTIFICATION MAP FOR DELTA LOBES OF THE MISSISSIPPI INVIX iAAP L A WINAS PLAIN /Not: TECHEs 1, 2. 4 Be- ST. BERNARDe 3 5,7,8,9, 11 4LAFOURC"Es 6, 10, 12, 14, 15 PLAQUEMINES-MODEM4, 0- Nt' k) so 4 .0 14 to '16 .7 14 A 13 C c 0 k 44RINCOIJ 14 I" DELTA COMPLEX SOURCE GAGLIANO a VAN BEEK FIGURE 3.5 TIME SEQUENCE"FOR MISSISSIPPI DELTA LOBES THOUSANDS OF YEARS BEFORE PRESENT ol 14 tj c@ PLAQUEMINES- MODERN DELTA COMPLEX MISSISSIPPI RIVER BAYOU LAFOURCHE BAYOUS LAFOURCIII,' ANI) 7'1;'I?RI71101vxt: LAFOURCHE BAYOU BLACK DELTA COMPLEX BAYOU BLUE -'RRFnONNE BAYOU T1. BAYOU SAUVACh.' co AfISSISSIIIIII-IA LOVTRF ST. BERNARD DELTA COMPLEX -BAYOU DES FAMILIES r-n BAYOU TERRE AUX DOEUFS w MISSISSIPPI RIVER AND BAYOU LAFOURCIIE CYPREMORT TECHE DELTA COMPLEX BAYOU TECIIH MARINGOUIN DELTA COMPLEX SOURCE, GAGLIANOSiVAN BEEK(1970) The natural levees extant in our region include those of the Lafourche, St. Bernard and Modern deltaic lobes. The inter-distributary basins are the Pontchartrain, Barataria and Terrebonne Basins (see Chapter 6). The processes leading to the fomation of these features are discussed in the following sections. Factors Affecting the Current Landscape There are four main factors affecting the landscape that have interacted to create the current landforms of our region. These are: 1. Sediment Deposition 2. Erosion 3. Subsidence 4. Man-Made Alterations Sediment Deposition The delta building process created the existing landfonns by deposi- tion of sediment first under water, then on the surface on the delta's own sediment base. After the delta floor reached the level of the sea, a system of ridges and basins formed a part of the deltaic plain. The alluvial ridges called "natural levees" were fomed when the river flooded during the springtime. Heavy suspended sediment (silt) was dropped as soon as the flow rate of water decreased as a result of overbank flooding. Later, vegetation also helped to hold back sediment. The mature resultant landform consisted of the river flanked by two ridges of silt, gradually sloping away from the channel (reflecting the decreased sediment deposition away from the main distributary). Deposi- 43 tion in the inter-distributaxy basins consisted mainly of fine clays and thus deposition here proceeded at a slower rate. The historical settle- ment patterns in the South Central Region reflect a linear pattern coinciding with these higher-drier ridges of good alluvial silt deposits (see Part II, Chapter 1). Erosion and Subsidence Wo processes that run concurrent with, and continue after delta building in coastal Louisiana, are subsidence and erosion. Erosion of the deltaic deposits com from the sea, mainly during intense stom periods. After deltaic deposition slows or stops in reaction to a shifting river channel, erosion rapidly reclaims much of the area that was once land. As waves, especially during storms, erode the coastline of an abandoned deltaic.plain, features known as barrier islands are produced. Barrier Islands have been defined as: Elongate, thin structures parallel to the shoreline of unconsolidated sedini-ents (usually sand) . . . They are separated from the marshland by estuarines and wetlands * * . and are generally located in areas with low sloping coastal plains and moderate tidal range. Conservation Foundation (1976), page 1. The main factors shaping the barrier islands of Louisiana and other areas of the United States have been described thusly: 44 Barrier islands are dominated by energy stresses. Exceptional wave force, wind and tidal energies, and ocean flooding are the predominant factors which shape and regulate the barrier island ecosystem. As a result of these factors, barrier islands are extremely dynamic system, constantly subject to change. Seasonal and other regular cyclic fluctua tions in wave patterns and intensity combine with irregular ocean storms and hurricanes to form and reform island profiles. The beaches and dunes migrate in response to these fluctuations. Stom overwash periodically carries sand onto the island, leaving substantial deposits of new sediments. The result is that morphologically, the islands are in a continual state of influx. While we generally recognize the great impact that hurricanes have on barrier islands, I should errphasize that they play an equally important role in shaping the islands. Conservation Foundation (1976), page 1. In Louisiana the barrier island off the coast of Terrebonne and Lafourche Parish is derived from silt deposits from the current delta of the Mississippi River, as well as erosional revurking of old silt deposits. The stranded barrier beaches of Lafourche Parish were developed in a similar manner. These features serve as unique ecosyste-ns in themelves. They also protect the vulnerable maxshlands behind thErn from rapid erosion. Cur- rently, the barrier island conplexes in the South Central District are diminishing is size due to lack of sediment re plenishment and man-made alterations in the ecosystem. Natural subsidence originates frcm tvo factors; conpaction and geo- logic subsidence. 45 Structural geologic subsidence (see Chapter 2) has occurred for millions of years. The weight of overlying sediment contributes to this process. Compaction occurs as sediments "settle" or consolidate over time, thus lowering the surface level. The results of these bko pro- cesses is the eventual destruction of the entire deltaic landform once deprivation has ceased in the area. Man-Made Alterations Three man-made alterations to the natural system have served to speed up the destruction of the deltaic land mass that is the South Central Region. These are: 1. Levee-Building 2. Reclamation 3. Channelization of Wetlands Although the levee ridges are dry axeas for most of the year, artificial levees were built to prevent the occurrence of disastrous river flooding that constantly plaqued early settlers in the area. These levees also halted deposition of new sedimnt onto the deltas where they were built, thus preventing further deltaic developnent. Reclamation, which has occurred mainly in this century, attempted to expand settlement into the low-lying water covered basins flanking the natural levees. During the natural process of subsidence, peat (partially decomposed organic matter) accuTiulating on top of old sediments in the basins helped keep pace with subsidence and maintain a surface level near to man sea level. Once the land was drained and leveed, however, this peat oxidized and decomposed causing the level of the land to drop below sea level. The land must be kept dry by artificial means 46 (punps). Should the levees break, the area would revert to a shallow water body due to the artificial increase in subsidence brought about by the reclamation process. Channelization of wetlands in the inter-distributary basins for navigation and mineral exploration has contributed to land loss by several means. Erosion and salinity changes brought about by these straight deep channels have destroyed the vegetation that holds together the peat and clay deposits that make up the basins. Without this pro- tection most of the land succumbs quickly to erosion and is lost. (The man-made alterations to the landscape will be discussed further in later chapters.) Total land loss (natural and man induced) is currently esti- mated at 16-21 square miles per year in Louisiana. The Geologic Subsi- dence Rate is calculated to be approximately one foot per century from natural causes (Gagliano and Van Beek, 1970). Figure 3.6 is an illustrative example of a natural levee/basin structure of a deltaic lobe moving through the various stages of delta building and decay. Most of the delta lobes in our region fall to classes B and C. The upper more extensive ridge/basin structures are still intact while the lower ends of the delta have suffered the ravages of erosion and subsidence. Figure 3.7 illustrates the various landforms extant in the South Central Region at present. SUDMY It is apparent from the previous discussion that the entire region is a young dynamic geomorphological area, the features of which have shaped the patterns of settlenwent and the economic activity in the past and in the present. lbre details on human habitation and its effect on this enviromnent, can be found in Section II of this report. 47 FIGURE'3.6 LIFE CYCLE CROSS SECTION OFA DELTAIC PLAIN PRESH MARSH ORGANIC MUCK GULF FLOOR @511@TY LA y INITIAL. DEVELOPMENT OF DISTRIBUTAR TARY TROUGH. SLIGHTLY BRACKISH MARSH FRESH MARSH INITIAL PEAT ------- NArU AL. LEVEE 4 t' T @TE@. JST@Rlj U, A@Y,TROUGH F@LL] Of TERICRATINGI- AN C4 , NEL,FILL, @N ENLARGMEXT OF PRINCIPAL DISTRIBUTARY AND ITS NATURAL LEVEES - CREATION OF MARSHES IN TROdGH. le, SRAC!:ISH MARSH 7- .5,A, NATURAL LEVEE 4 C MAXIMUM OEYELOPMENT OF DISTRIBUTARY ANL) ITS NATURAL LEVEES -CREATION OF SWAMP AS LEVEE SUBSIDES. SWAMP BRACKISH MARSH NATURAL LEVEE D. DETERIORATION OF DISTRIBUTARY -ADVANCE OF SWAMP OVER SUBSIDING LEVEES. -BRACKISH MARSH SALINE MARSH---I' lu -j 3AY OR SOVNO 7k N _7_ 1@ T 11- E F-_ 51 T 5 NATURAL oo LEVEE CONTINUED SUBSIDENCE WITH PARTIAL DESTRUCTION OF MARIMES. SOURCE: GAGLIANO 8 VAN BEEK (1970) 48 FIGURE 3.7 GEOMORPHOLOGICAL FEATURES ..... ... ... . ...... ....... . MA PREPA LAKE PONICHARTRAIN ........... ............... .. ........ ........ ........ :.. ......... ............ . .......... --X ................ X: .... ... ................ NXI. ........... A ............ ............ ............ 6-h PLEISTOCENE TERRACE FLATLANDS & BASINS NATURAL LEVEE 1 0 10 20 30 4 MILES COASTAL MARSH ESTUARINE BASIN SIDURCEj U.S. Corps of Engineers (1973) and NOTATION OF ACCURACY Drafting Section of South Central BARRIER ISLANDS a BEACHES THIS MAP IS TO BE USED FOR PLANNING Planning Development Commission(1980) PURPOSES ONLY. SURVEY MEASUREMENTS DISTRICT BOUNDRY ARE WT TO BE MADE FROM THIS MAP. N. @PA. R BIBLIOGRAPHY Gagliano, S. (1973) Hydrologic and Geologic Study of Coastal Louisiana Report No. 14: Canals Dredging and Land Reclamation in the Louisiana Coastal Zone. Center for Wetlands Resources, L.S.U., Baton Rouge, Louisiana. Gagliano and Van Beek (1970) Hydrologic and Geologic Studies of Coastal Louisiana, Report No. 1: Geologic and Geomorphic Aspects of Deltaic Processes, Mississippi Delta SystEM. Coastal Resources Unit, Center for Wetlands Resources, L.S.U., Baton Rouge, Louisiana. Gagliano S. et al (1973) Hydrologic and Geologic Studies of Coastal Louisiana, Report No. 18: Volune I, II: Envirowxental Atlas and Multi-Use Management Plan for South-Central Louisiana. Center for Wetlands Resources, L. S. U., Baton Rouge, Louisiana. Morgan, Joel David (1977) Geoscience and Man Volume XVI - The Mississippi River Delta: Legal Geomorphological Evaluation of Historic Shoreline Changes. School of Geoscience, L. S. U., Baton Rouge, Louisiana. The Conservation Foundation (1976) Barrier Islands and Beaches: Technical Proceedings of the 1976 Barrier Islands Workshop. The Conservation Foundation, Washington, D. C. U. S. Army Corps of Engineers (1973) Inventory of Basic Enviromi-ental Data: South Louisiana. Engineer Agency for Resource Inventories, U. S. Army Engineer Topographic Laboratories, Washington, D. C. 50 CHAPrER 4 - SOILS 13Y Jarms B. Edmonson INIRODUCTION In general, soil refers to the loose surface of the earth as dis- tinguished from solid rock. The four components which make up all soils include: mineral matter, organic matter, water, and air. For example, an ideal soil for gardening purposes would be as follows: mineral matter - 45 percent; organic matter - 5 percent; water - 25 percent; and air - 25 percent. Soils undergo continual change, which escapes a casual study of soil. Each soil has a life cycle in terms of geologic time. This evo- lutionary nature of soil is effected by climate and living matter (plants and animals), acting upon parent niateria.1 as conditioned by relief (slope) over periods of time. As soils develop, they stratify into layers called horizons. Typically there are three,general horizons: A, B, and C (Floth, 1972). The nature of the parent material, slightly altered or weathered material from which soil is formd, has a decisive effect on a soil's properties. These properties of the soil include texture (sands, silts, or clay), mineralogical composition, and degrees of stratification. In South Central Louisiana, the parent material is derived from water- deposited sediments, or alluvium. 51 Alluvial-deposits are scattered into narrow, irregular strips bor- dering streams, rivers and bayous. A common characteristic of this parent material is its stratification layers of different sized particles overlying each other. Mineralogically, alluvium is related to the soils which served as a source of material. Most alluvium is carried and deposited during floods. It is at this period that erosion is most active and the carrying capacity of streams is at a maximum. When a flooding stream or bayou overflows its banks, its carrying power is suddenly reduced as the flow area increases and velocity decreases. This causes the coarse sands and gravels to settle along the bank, where they form conspicuous ridges called natural levees. As the water reaches the back swamp or bottomland, the rate of flow is slow enough to permit the silt to settle. Finally, the water is left in quiet pools or marsh areas, from which it depoits the fine clay. Levees are characterized by good internal drainage during periods of low water, whereas the back swamp and marsh exhibit poor internal drainage (see Chapters on Drainage and Geomiorphology). Two orders of soil occur in South Central Louisiana. These are the Histosols (organic soils found in the wetlands) and the Inceptisols (mist soils found along the drainage ways). The suborders most typi- cally found in this region include: H2-Saprists, made up of decomposed mucks; and 12-Aquepts, seasonally saturated with water. The Saprists are generally good for truck crops if drained, but axe usually left idle when undrained. The Aquepts are gently sloping and if drained, support most raw crops including corn, soybeans, sugarcane and cotton. If left undrained, Aquepts soils are most commonly used as pasture or woodlands (Ibth, 1972). 52 GENERAL SOIL TYPES , The general soil types and associations found in South Central Louisiana are distributed and controlled directly by the gecmorphic features of the landscape. These natural features include: levees; backswanp; bottornland; drained swamp; drained marsh; fresh marsh and pond; old distributary bayous and natural levees; brackish marsh, lake, bay or pond; beach ridge; and salt marsh. Table 4.1 displays each soil association, its characteristics, suitability, degree of limitation, engineering characteristics, management, drainage factors and existing usage (Gagliano, 1973). Figure 4.2 shows the distribution of these soil associations through- out South Central Louisiana. However, if one desires a more detailed study of the soils in our region, the U. S. Soil Conservation Service has soil surveys for five of our parishes, excluding St. Charles. In conclusion, much consideration must be given to the soils located in South Central Louisiana, their distribution and properties, when guiding future development. Characteristics such as bearing capa- city, shrink/swell potential under modified ground water levels, and ' trafficability place distinct constraints on the expansion of urban type development. When ignored, development may either fail as manifested in a number of reclamation projects or result in unwanted maintenance and flood protection requirements (Gagliano, 1972). 53 TABLE 4.1 OLD DISTRIBUTARY DRAINED BACKSWAMP LEVEE BAYOU 8 SWAMP BEACH BRACKISH MARSH NATURAL LEVEES 'S- D@@? S01 LS @FR TOMLAND LI-1 SALT RIDGE LAKE,8AY,. MARSH OR P. POND @av 0:1611:11m UMW AUJJVIAL GyprIE101117 onownt-elity FIES"'ATER oDn-nt-towry YAMI 111MOWD SIVJM SWAW (TVVENT SWAW turtics alluvial SOIL utoon poll- MAINED MAINIM bad-in st- t.] sh.,key FFMMI/SMX SWASIP bwtmry baidin ASSOCIATION UMMMM &U.71FAM HAM smo mvXXIS" timm lbld@l!' dundee VA" -I- lb_ia Organic layer of various fine imuid edsd -table on. teri.3 milt loss ururtble: -9-1c organic wate- thin o@ic thin onmic clay anrfaCe silt I.- :-Itt= thicknes underlain by with shell ot thic aurlace astertal newral ',a, sawrej su,j"' unmi, surface under- and ab8ot I -I. by clay: derI.Ja below w, spo GENERAL suit dwp`rmed uillme clays lompreote underlain by R." feet thick. md- feet. thick. lain by clay. 1 25" by 1-: silt clay wry Its. to 'Ity clya wMI f"t thick o to ofI I- Ld. fine I-am _k silt clay lain by silty CIO- underlain by with tb .it 7 cl sys with with -,ti- when loodad o- &ub- Ith sep-ti- clay! son, f -Zled e7st wpa,stim when fl..,hd: -11 at- flooded: this Iowny thick pal- mtert titanic W.t - wuck underlain by t o',:T: .Ilghtl -fluid his* .,x-ic fill mtertLl. flues, lonsf SOI L c,.Y. v lim to send -is .1 2-9' thick it. t,ace 1.1 and I to yr .-r -11 cl": wesural ,w,,rsonent, high water table pe,annently high water table fl.t.tl-. fast thick it- a-d- fluid cj.y.. CHARACTERISTICS Pernanontly high @ter table prumnent high water table SUITABILITY 7m SDIL not amitab)e hot suitable hot suitable art, suitable not suitable not suitable not suitable not suitable %uM-f&lr fel HIQIWAY SUPKMX not suitable fair hot suitable 1.1-ponr not suitable not -Itbl. not suitable not -liable not suitable fal,-poor good-fair HIGIwAY SWFASE not atiltblo fair not wmlt@hle fair not suitable not suitable hot suitable not suitable not indt-bt. fair fair FOSTIMITUIL rill, not suitable not suitable not suitable ftir-poo@ not sW table not suitable not suitable not _ltbl, not votgbl. ftir-poo, tlir SAND OR SHEIL not -liable good not -liable not sud table not suitable not suitable not suitabis not -liable not suitable not suitable gwd-fiy (Gut@faoe feat@) DEGREE OF LIMITATION wry k 't to --ts II)WESIMS (1-2 wry) wry se,wre severe wry we - re alight to -tP "T7 ws-pu se - - slight to -wm to -1 .- -r" 21 &@ Ll!qM. UOLUM very movers Saw- wry anue's .&-is to @@ -" wwm - light to -_ ww"m to wry Se"re "Vep, .rxierw . to se-_ (with -Ity -M s)stes) 91101L to nodknate -7 -M ""ps :3 tttt to wwm mwl* to wry "-r`e -wm slight to aodumtO LANWAT`F--GAfM,'&-tANE5 wry sew" awwre wry PIAY(1ff)Uffr,-PIMC ARM wry _w wry se ve re -&rate to sawre wry as - - ft"m sligLt to sewpa mwm to wry severe vewpa noderate fnM.1--AWT-AlRP0W FUMAYS wry iwrwpe --w wry severe noderat. wry -.- severe .1lidt to --.- sw-m to wry sa-m mwm noderate CANISFUZ-OW FAIINAYS very @re ry se - - slight to vadente wry sewre sevepe 'milidit to severe wow. to SeVers se-pe alight to anlerate ENGINEERING CHARACTERISTICS SIMITFIACY rOU241AL high low high las high wry'high wedlua SIMINK-Swal, IMIMIAL I- to high high high Iow Id gh high high high wry - nodersts BEARING Mmxmi low - wry Im high Iow - wry low Iow Icw _ry I- low Icw - nuderst. (1-2 -ry boildl.g,) CMIXIC111 POMITIAL high high hIF% hich .*-is dewr d- hrb., facklitt- ducks -tfldb dew, duck. duck, ducks duck. nartme-type installations MANAGEMENT dear swashore birds doe, ducks de, craw(Ish turinry, ducks. PI-I., rabbits squirrels rabbits, hves. 1.uwIl q..l I =1mjd"d' DRAINAGE fl,,oding foorly drained foorly drained ma, le-1 p-ly drained poorly drulned I.-I P_rly dmfn@ skiiihtly wt ild-ters near saw le-I wet to intreT . t FACTORS -derately wet f lod. re.tilential. I iwatm*. m pastum/ranw urban wildlife cropland. rec-timal. p,,,IdentIal. -tIdIIM hk,it.t bird santuary wildlife -it i-rod -bi. 1.1hi'tai h.,,It.t pautum. c-P, t_' crops, niarrana. -,d)-d. urban. -t"tl-. I j EXISTING USEAGE re.-tion urban tpkhei- being cleared trubustrial -111,112. Irlidlife. torroa Mdu trial fill SOURCE: GAGLIAN08NAN BEEK (1973) FIGURE 4.1 S01 LS OF SOUTH LOUISIANA LAK LAKE PONTC4ARTRA00 z Y@y c@ "No "7- j" -Z y J@ 1-1b ALLUVIAL SOILS (NOtUld Lev"s- River VdIleYsl UM PLEISTOCENE -TERRACE (Older uplands) BASIN SOILS: Swamp Forest/ Bottomldrd Clay Base Soils MARSH/ SWAMP ORGANIC SOILS NOTATION OF ACCURACY THIS MAP IS TO BE USED FOR PLANNING BEACH RIDGE I BARRIER ISLAND (Silts. a SOnds) PuRPOSCS ONLY. SURvEY MEASUREMENTS ARE NOT TO BE TAKEN FROM THIS MAP, SOURCE U.S. Army Corps of Engineers (1973) and DISTRICT BOUNDRY Drafting Section OfSouthCentral Planning and Developiwt commission ((9801 FIGURE 4.1 S01 LS OF SOUTH LOUISIANA nil pil T@7 MIN AKE A, REANS- LAKE PONTCHARTRAIN . . . . . i i i . . . . . . _k` & 14 - @ep' 010 4jk4 ALLUVIAL SOILS (Natural Levees-River Valleys) PLEISTOCENE TERRACE (Older Uplands) BASIN SOILS: Swamp Forest/ Botiomland clay Base Soils 10 0 to 20 MARSH /SWAMP ORGANIC SOILS NOTATION OF ACCURACY THIS MAP IS TO BE USED FOR PLANNING BEACH RIDGE / BARRIER ISLAND (Silts 8 Sands) PURPOSES ONLY. SURVEY MEASUREMENTS ARE-NOT TO BE TAKEN FROM THIS MAP. DISTRICT BOUNDRY SOURCE: U.S. Army Corps of Engineers (1973) and Drafting Section of South Central Planning and Development Commission (1980) BIBLIOGRAPHY Foth, H. D. and Turk, L. M. (1972) Rmdamentals of Soil Science. New York: John Wiley and Sons, Inc. Gagliano, S. M. and Van Beek, J. L. (1973) Environmental Atlas and Multi-Use Management Plantor South Central Louisiana; Report 18. Center for Wetland Resources, Louisiana State University, Baton Rouge, Louisiana. 56 CHAPFER 5 - NATURAL VEGEFATION By Edwin J. Durabb INTRCDUCTICK Vegetation in the South Central District, like elsewhere, is in- fluenced by the factors of geomorphology, soil type, elevation, wetness and climate. These processes, discussed in this report, have shaped the location and type of natural flora in the region. The vegetation zones in the South Central District can be broken down into: Forested - 1. Natural Levee Vegetation - 2. Backsm@uT Non- - 3. Fresh Water Marsh Forested - 4. Brackish Marsh - 5. Saline Marsh Itixed - 6. Beach Ridges/Barrier Islands - 7. Spoil Banks The following is a brief discussion of each general vegetation type within the district. 57 FORESTED AREAS Natural Levee Vegetation The natural levee vegetation is that characteristic of the higher, drier, alkaline, silty upland soils of the distributary system of the Mississippi Delta. The natural vegetation originally consisted of forest lands, usually hardwoods, mainly oak. The following were the dominant form of vegetation on these surfaces (Detro and Davis, 1978): 1. Live Oak 2. Water Oak 3. Red Gun 4. American Elm 5. Honey Locust 6. Pecan Due to the fertile nature of the soil, relatively good drainage, and lack of flooding except during the spring, this area was rapidly cleared and settled. Today, most of the population of the South Central District resides in these areas. The land has been cleared and farrwd for sugarcane, soybeans and truck crops. Almost no hardwood forest that originally grew on the natural levees remain. Backswamp According to Bahr and Hebrard (1976), a swamp is: a woody commmity occurring in an area where the soil is usually saturated or covered with water for one or more months of the growing season. The vegetation in the swamp forest is characterized by tree growth, the type of which is dependent on the slight differences in elevation and soil type that govern the degree of standing water in the area. 58 The swairp forest flanks the natural levees and fills the inter- distributary basins limited only by soil type and salinity levels. This is largely an inundated fresh water region (see Chapter 7 for full dis- cussions of the wetlands ecosystem). Table 5.1 lists the dominant vegetation types and percentage of cover of the two main types of swamp forest vegetation. Type one forest occupies the wetter areas; type tvu the drier zones. This table is based on a survey in the Barataria Basin and may differ somewhat from other areas. However, the main species in the vegetation zone are mre or less the same. 59 TABLE 5. 1 Percentage Of Tree Species In Cypress-Tupelo Gun Swanp And Bottomland Hardwood Fbrest Of 'Ihe Barataria Basin Cypress-Tupelo Gum Swamp Taxodim distichum (Cypress) 33.33 Nyssa Aquatica (Tupelo gum) 32.41 Acer Drumnondii (Swamp maple) 19.44 Fraxinus; tomentosa, (Pumpkin ash) 8.33 Bottomland Hardwood Forest Acer drumiondii (Swamp maple) 25.00 Nyssa, Aquatica (Tupelo gum) 11.43 Acer negundo (Boxelder) 7.86 Populus; heterophylla (Cottonivood) 2.86 Taxodium distichum (Cypress) 4.29 Cornus drum-nondii (Roughleaf dogwood) 8.57 Salix nigra (Black willow) 5.71 Ulmus americana (American elm) 5.00 Carya ovata (Shagbark hickory) 4.29 Fraxinus tomentosa (Pumpkin ash) 3.57 Quercus nigra (Water oak) 2.14 Celtis laevigata (Hackberry) 2.14 Diospyros; virginiana (Persim-non) 3.57 Ilex decidua (Deciduous holly) 2.86 Quercus shumardii (Shumard red oak) 2.14 Source: Bahr and Hebrard (1976): 16. 60 NON-FORESM AFEAS Marsh Vegetation Marshland has been defined as: a periodically flood zone characterized by primarily nonwoody vascular plants. Bahr and Hebrard (1976): 23. This vegetation type makes up the bulk of the land cover in Terre- bonne and Lafourche Parishes and significant areas in St. Charles (Louisiana State Planning Office, 1975). These wet grassland areas are generally poorly defined and tend to merge into each other rather than exhibit sharp contrasts between zones. Soil structure and salinity define the marsh forest contact zone. Water salinity concentrations and the resultant vegetation types are used to delineate the three classifi- cations of Fresh, Brackish and Saline marsh. The following is a discus- sion of each marsh type. Fresh Water Marsh Fresh marsh is characterized by the most diverse plant conrmities of all, the marsh units. It is also the most ambiguously defined area. Much of this zone is represented by a phenon-enon known as "flotant marsh": Flotant consists of a dense mat of vegetation supported by detritus several feet thick, which is held together by a matrix of living roots. This floating marsh is indistinguishable from true wetland until trod upon and extends from the shoreline of a lake into the lake itself. Eventually, as the bottom sediments and the floting layer each accumulate more material, they merge to form a new shoreline and the lake shrinks in size. Bahr and Hebra-rd (1976): 24. 61 Fresh marsh vegetation cover often occurs over huge areas of peaty deposits. The soil mix is often sixty-five percent organic and thirty- three percent clay.(see Chapter 4). Representative plant species are listed in Table 5.2. 62 TAELE 5. 2 Percentage of Plant Species In F'resh Maxsh Portions of Barataria Basin Panicun hemitomon (Maidencane) 41.35 Sagittaria falcata (Bulltongue) 17.42 Eleocharis sp. (Spike rush) 12.31 Alternanthera philoxeroides (Aligator -weed) 3.43 Cyperus odoratus (Sedge) 3.21 Typha spp. (Cattail) 2.59 Echinochloa walteri (Water rrdllet) 2.15 Eichornia crassipes (Water hyacinth) 1.99 Bacopa monnieri (Water hyssop) 1.82 Polygonun sp. (Snwtweed) 1.60 Scirpus olneyi (Three-cornered grass) 1.48 Zizaniopsis miliacea (Giant cutgrass) 1.36 Source: Bahr and Hebrard (1976): 25. 63 Brackish Maxsh Brackish marsh is the axea between the fresh and saline marshes in the coastal estuarine system. This zone is extremly important ecologic- ally, as it provides a vital link in the estuarine salinity, water flow and flood chain systems. The brackish marsh system represents the first marsh unit strongly influenced by tidal effects. This area also receives freshwater runoff from other units as well. (Bahr and Hebrard 1976) have stated that aquatic areas that are the most stable, i.e. unvarying with respect to their physical characteristics, especially salinity and temperature, are mre likely to show greater specie diversity than areas of rapid change. Therefore, this 'area has somewhat less plant variety than fresh marsh. Table 5.3 illustrates the typical plant commmity of a brackish marsh. This type of marsh is the first vegetation zone that meets conmnly accepted definitions of estuary. Two of the definitions are: An estuary is any confined coastal water body with an open connection to the sea and a measurable quantity of salt in.its waters. Clark (1975): 1. Estuaries are defined as inland bodies of water intermdiate between fresh and saline system and therefore mixing zones. Bahr and Hebrard (1976): 34. Since the brackish unit is covered with water with measurable salinity content, it marks the beginning of the transition between freshwater and marine environments (see Chapter 7 for a discussion of the Wetlands Ecosystem). 64 Soils in this unit have as little as 16 - 30 percent clay content and have the highest level of organic content of any maxsh unit (see Chapter 4). C, 65 TABLE 5.3 Percentage of Plant Species In Brackish Marsh Areas of Barataria Basin Spartina patens (Wire grass) 45.84 Distichlis spicata (Salt grass) 28.96 Spartina alterniflora (Oyster grass) 9.03 Eleocharis parvula (Dwarf spikerush) 5.49 Juncus romerianus (Black rush) 3.26 Scirpus olneyi (Three-cornered grass) 1.26 Source: Bahr and Hebrard (1976): 36. 66 Saline Marsh Saline marsh has been characterized by Bahr and Hebrard (1976) as in a declining state, i.e. in transition between wetland and open water. The area that is now saline marsh in the.South Central Region was at one time brackish or possibly even fresh during the period when delta building and large quantities of freshwater and sedilwnt were introduced into this zone. The waters of this zone are almost marine with a diurnal tide range. Hurricane stonn surges and waves affect this area hardest causing considerable land loss by erosion. The only protection this area has is the barrier islands and beach ridges that provide partial shelter from wave energy. As in the other marsh types, organic levels in the soil are high, but not as high as brackish and fresh marsh. The remainder of the soil is usually fine clay. Species diversity is low and confined to those plants tolerant of high salinity. Table 5.4 lists the primary vegetation types in this zone. 67 TAME 5. 4 Percentage of Plant Species In The Saline Marsh Region of Barataria, Basin Spa.rtina alterniflora, (Oystergrass) 62.79 Juncus romerianus (Black rush) 14.90 Distichlis spicata, (Salt grass) 10.05 Spaxtina, patens (Wire grass) 7.77 Source: Bahr and Hebrard (1976): 68 MDCED AREAS Beach Ridges/Barrier Islands Barrier islands and beach ridges present a unique and varied habitat ranging from marsh to upland forest vegetation zones. Plant species are too numerous to mention here. The following is a brief listing of habitat zones common on Louisiana barrier islands (Bahr and Hebrard 1976). 1. Salt marsh habitat (along leeward edge of island). 2. High marsh (transition marsh located on higher ground). 3. Forest (located on highest ground only on larger islands with vegetation resembling that of the natural levee forest. 4. Meadow habitat (located toward the Gulf next to the wooded area). 5. Dune habitat (located in the area close to the Gulf capable of supporting rooted vegetation). 6. Mangrove - (tree vegetation in coastal Louisiana confined to a Low Bush conmnly found only along the coast (limited by intol- erance of cold weather. Spoil Banks Due to the numerous canals duo, for navigation and oil and gas ex- ploration, there exists many long ridges parallel to these canal borders of dredged sediment called "spoil banks". Soils on these banks can be of any type and the vegetation is dependent on the age of the spoil bank-, soil type and height of the ridge. The most commn vegetation, woody and nonvoody, are listed in Table 5.5. 69 Table 5.5 Plant Species Composition Of Spoil Banks And Natural Levees in Coastal Louisiana Baccharis sp. (Groundsel tree) Iva frutescens (Marsh elder) Cynodon dactylon (Bermuda grass) Spartina, patens (Marshhay cordgrass) Distichlis spicata, Phragmites commis (Roseau cane) Rubus sp. (Blackberry) Trees (when present) Salix nigra, (Black willow) Sapium sebiferm (Tallow tree) Source: Bahr and Hebrard (1976): 63. 70 SUMMARY The vegetation of the South Central Area has developed in response to deltaic deposited sediment, subsidence, erosion, climate and estuary development. Figure 5.1 illustrates the location of the main vegetation zones in the'South Central Area. It should be noted that, for clarity sake, all marsh units and spoil bank vegetation are not shown. 71 VEGETATION OF SOUTH LOUISIANA . . . ....... ITTRI TT T1 PT . .. . . . . . . . T, "'I a MAUREPA ,X. LAKE PONTCHARTRAIN !p@ \Z\ Z Z \z N \ZZ"" DISTRICT BOUNDARY NATURAL LEVEES (VEGETATION & CROPS) URBAN a BUILT-UP AREAS FRESH WATER'MARSH SALT WATER MARSH BRACKISH WATER MARSH EVERGREEN FOREST SWAMP FOREST AREA MIXED FOREST AREA SOURCE U.S. ARMY CORPS OF ENGINEERS NOTATION OF ACCURACY (1973) AND DRAFTING SECTION OF THIS MAP IS TO BE USED FOR PLAN14ING SOUTH CENTRAL PLANNING AND DEV- PURPOSES QhLLY. SURVEY MEASUREMENTS ELOPMENT COMMISSION (1980). ARE NOT TO-BE MADE FROM THIS MAP. BIELIOGRAPHY Bahr, L. M. and Hebrar , J. J. (1976) Barataria Basin: Biological Cbaracterization. Center for Wetland Resource, Louisiana State University, Baton Rouge, Louisiana. Clark, John (1974) Coastal Ecosystem : Ecological Considerations for the Management of the Coastal Zone. The Conservation Foundation, Washington, D. C. Detro, Randall and Davis, Donald (1978) "Bayou Lafourche", from Kesel, R. and Sander, R (1978) A Field Guide Book for Louisiana. The Association of American Geographer, Washington, D. C. Louisiana State Planning Office (1975) Land Use Data Analysis Program. U. S. Geological Survey and Louisiana State Planning Office, Baton Rouge, Louisiana. 73 CHAPTER 6 - DRAINAGE AND GROUNDWArIER RESOURCES By Edwin J. Durabb INTRODUCTICN Water and water flow patterns are of prime concern in this area due to the low land elevations and constant flood threat from rivers and the Gulf of Mexico. The patterns of drainage and water distribution are determined by five main factors: 1. Local Geomorphology 2. External Influx of Freshwater 3. Rainfall 4. Ocean Tidal Waters 5. Man-made Alterations. Local Geomorphology shapes the flows of water in the basin. `Ihis topic is discussed in detail in Chapter 3. External Influx of Freshwater into the district occurs from the Mississippi River distributaxy system and drainage off of the higher Pleistocene terraces to the north of the district. Rainfall currently provides the majority of the freshwater supply in the estuarine drainage basins since man-made levees have limited Mississippi River water input (see Chapter 1). Ocean Tidal Waters flow into all basin areas from the Gulf of Mexico causing the ,conditions in the basins to be labeled estuarine. Finally, Man-made Alterations such as canals and levees have changed water flow patterns in the area (see Paxt II, Chapter 5 for further discussion). Groundwater in the district occurs mainly in shallow aquifers and is not suitable for large scale use. Salt water is a problem for water 74 supplies as one approaches the coast. A full discussion of drainage patterns and groundwater is presented in the basin descriptions that follow. DRAINAGE BASINS Data collected by the Louisiana 208 Water Quality Program has enabled the South Central District to be separated into four main basins: 1. Terrebonne 2. Barataria 3. Pontchartrain 4. Lower Mississippi. None of these basins lie entirely within the South Central District (see Figure 6.1). The following is a discussion of each of the drainage and groundwater chaxacteristics of these major drainage basins. Lake Pontchartrain Basin Physical Description Basin Boundaries The State of Louisiana has been divided into twelve major drainage basins for the purpose of water quality management planning. The Lake Pontchartrain Basin is located in southeastern Louisiana as shown in Figure 6.1. The basin is bound by the Mississippi State Line on the north, the Mississippi River east bank levee on the west, the drainage divide on the Pearl River Basin on the east, and the Mississippi Sound on the south. 75 FIGURE 6.1 M I S S I S S I P P I Iol PONTCHAR+MN BASIN cm-pan Ron. Picayune LAKE NIALPIE103 L4KE PONrCHAR MAI. . . .... . . . . . . . . . 4@ L r Pd&r.di. 41,v % 41?7q .zs TERREaMNE BASIN % io/ Ilk SOL1111CE: LA. VALDLWE AND SCALE 1:500,000 NOTArION OF ACC BASIN BOUNWY-miiiiiiiiiiiiiiii, FtMRIE3 COMOWK(Iftill) THIS MAP ISS TO BE USED DISTRICT BOUNDARY-111111111111111111111111 DRAINAGE BASINS PURPOSES QW. SURVEY ARE NOT TO BE MADE Hydrology - Surface Water The Lake Pontchartrain Basin consists of the tributaries and dis- tributaries of Lake Pontchartrain. Lake Pontchartrain is a brackish natural lake and has tributary drainage area of approximately 4,900 square miles. Most of this basin lies north and east of the South Central District. Only the northern portion of St. James, St. John and St. Charles Paxishes are within the basin boundaries. Major tributaries draining into Lake Pontchartrain are the Tangipahoa and Tchefuncte Rivers, Lake Maurepas, and Bayou Lacombe, Bonfouca, and Castine. The Bonnet Carre Spillway serves as an intermittent source of inflow when used for flood control on the Mississippi River. The drain- age systems of Jefferson and Orleans Parishes discharge storm flows into the lake on the south shore. Tributaries discharging into Lake Maurepas include the Blind, Amite, and Tickfaw Rivers. Pass Manchac links Lake Maurepas to Lake Pontchartrain. The Rigolets and Chef Menteur Pass are natural distributaries on Lake Pontchartrain which discharge to Lake Borgne. The Inner Harbor Navigation Canal, the Intracoastal Waterway, and the Mississippi River Gulf Outlet axe man--imde navigable waterways that inter-link the Missis- sippi River, the Gulf of Mexico and Lake Pontchartrain for comercial shipping operations. Me Louisiana Stream Control Carrnission has divided the Lake Pontchartrain Basin into sixteen stream segments. Each designated segment represents the drainage area of a particulax watershed. Table 6.1 outlines the stream segments in the Lake Pontchartrain Basin. 77 TAELE 6. 1 Lake Pontchartrain Basin Stream Segment Description Comite River from Mississippi state line to the Amite River including all tributaries. Bayou Manchac to confluence with Amite River, including Dawson Creek, Ward Creek, Bayou Braud and all other tributaries. Amite River from Mississippi state line to Lake Maurepas including all tributaries to Lake Maurepas. Bayou Conway, Bayou Black, and Blind River and related tributaries to Lake Maurepas. Tickfaw River from Mississippi state line to Lake Maurepas including Ponchatoula Creek, Natalbany River and all other tributaries. Lake Maurepas and tributaries including Pass Manchac. Tangipahoa River from the Mississippi state line to Lake Pontchartrain including all tributaxies. Tchefuncte River from headwaters to Lake Pontchaxtrain including Bogue Falaya River and all other tributaries. Bayou Lacorrbe from headwaters to Lake Pontchartrain including tributaries and related watershed. Bayou Bonfouca from headwaters to Lake Pontchartrain including tributaries and related watershed. Lake Pontchartrain including minor tributaries; Bayous Castine, Chinchuba, and Cane. Lake Catherine, Rigolets and Chef Menteur Pass and ancillary waterbodies including Intracoastal Waterway from Chef Menteur to Rigolets Pass. Inner Harbor Navigation Canal from Mississippi River to Lake Pontchartrain. East/West Intracoastal Waterway from Inner Harbor Navigation Canal to Chef Menteur Pass. Mississippi River Gulf Outlet from Intracoastal Waterway to Breton Sound and tributaries including Bayou Bienvenue and Bayou Dupre. Coastal waters of Lake Pontchaxtrain Basin including Lake Borgne, Mississippi Sound, and numerous lakes and enbayments in the control marshes of St. Bernaxd Parish. Source: Stanley Consultants (1979) page 2, 3. Partly within South Central District. 78 Groundwater Groundwater is confined within late Quaternary (Recent and Pleistocene), early Quaternary (Pilocene), and Tertiary (Miocene) deposits to minus 2,000 feet MSL or more. Almost all groundwater wells north of Lake Pontchartrain exhibit axtesian behavior because of the confining sand and clay subsur- face strata. Water-bearing sands at various depths have been differentiated and are denoted by aquifer depth, for exanple, "the 400 foot sands". Most aquifers are connected hydraulically and movement of groundwater occurs rapidly within aquifers and to some extent among aquifers. This movement is primarily horizontal and down dip due to the inpermeable nature of the intervening clay layers. Miocene deposits axe recharged north of the study area where out- crops occur. Some Pilocene aquifer recharge occurs in upland outcrops within the study area, but this activity is limited to elevated upland areas with moderately permeable soil and subsoil layers. The younger alluvial aquifers axe recharged by rainfall, artesian discharge of under- lying, older groundwater deposits, and to some extent by fluvial recharge during high river stages. This activity is particularly evident with the Mississippi River alluvial valley sha-1low aquifers. With increasing inland elevation, fluvial recharge is the dominant recharge mechanism, and groundwater flow is primarily towards stream beds where it provides a portion of the base flow of the uplands rivers (Stanley Consultants, 1979). 79 Almost all of the productive groundwater areas in this basin are located north of the South Central District. Only the northern portion of St. John Parish has sufficient reserves of groundwater used for municipal use at this time (see Table 6.7 for sources of water usage in South Central Planning & Developnent Comission District. Terrebonne Basin Physical Description Basin Boundaxies The Terrebonne Basin (Figure 6.1) covers an area extending from New Roads and Morganza in the north to the Gulf of Mexico in the south and from Port Allen and Golden Meadow in the east to Morgan City in the west. It is approximately 120 miles long and varies from about 16 to 72 miles in width. The Mississippi River is the northern boundary, Bayou Lafourche and the Mississippi River are the eastern boundaries, the Gulf of Mexico is the southern boundary, and the East Atchafalaya Basin Protection Levee and the Intracoastal Waterway form the western boundary. This encompasses over 1,750 square miles, including all of Terrebonne Parish and portions of Pointe Coupee, West Baton Rouge, Iberville, Assumption, Ascension, St. Martin, St. Mary, Iberia and Lafourche Parishes. Basin Hydrology - Surface Water Surface water areas within the Terrebonne Basin conprise a complex combination of interconnecting rivers, lakes, bayous and canals. Most of this surface water is found in the southern half of the basin where coastal marsh and estuarine regions prevail. 80 A table of stream seguients can be found in Table 6.2. Major rivers and lakes are listed in Table 6.3 and Table 6.4, respectively. Navigable canals throughout the basin are numerous, the largest of which include the Intracoastal Waterway, the Port Allen to Morgan City Intracoastal Waterway and the Houma Navigation Canal. The Intracoastal Waterway has a project depth of 12 feet, is 125 feet wide and stretches 1,115 miles from Brownsville, Texas to Apalachicola, Florida, of which approximately 65 miles lie within the Terrebonne Basin between Morgan City and Larose. The Port Allen to Morgan City Intracoastal Waterway connects the 2 cities and is 12 feet deep and 125 feet wide. The Houma Navigation Canal runs 16 miles southward from the Intra- coastal Waterway at Houma and then southeasterly for 10.5 miles to the Terrebonne Bay. The canal has a project depth of 15 feet and extends to a width of 150 feet. Surface water flow over the basin is generally toward the Gulf. The shallowness of most of the water, particularly in the southern and coastal regions of the basin, creates flow conditions which are highly susceptible to tidal and aeolian (wind) influences. A corrbination of tidal factors and southerly winds, for example, may produce conditions of no flow, and in sone instances even a northerly flow. Interconnections between shallow bodies of water (bayous, canals, bays, marshland and estuarine areas) result in a different flow pattern for each set of wind, tide and rainfall conditions. During hurricanes, water can move inland -in vast quantities, endangering both life and property. 81 TAELE 6. 2 Terrebonne Basin Stream Segment Description Lower Grand River watershed from headwaters to Bayou Sorrell Lock includ- ing Bayou Grosse Tete and False River Lake and other tributaxies. Terrebonne Basin above Bayou Black Ridge and Little Bayou Black Ridge including Grand River, Belle River, Lake Verrett, Lake Palourde and Lake Bayou Black and tributaries. Terrebonne Basin above Bayou Blue Ridge including E/W Intracoastal Waterway from Houma to Larose, Bayou Blue, Bayou Grand Coteau and tribu- taries. Bayou Lafourche from Donaldsonville to Larose. West Terrebonne coastal zone south and west of Bayou Black Ridge and Bayou du Large Ridge including E/W Intracoastal Waterway from Bayou Boeuf to Houma, Lake De Cade, Lake Merchant, Bayou Junop and adjacent coastal waters. Middle Terrebonne coastal zone between Bayou du Large Ridge and Bayou Terrebonne Ridge including Bayou Grand Caillou, Houma Navigational Canal, Bayou Petit Caillou, Bayou Terrebonne and Lake Pelto and adjacent coastal waters except Segment 1213. Estuarine area south of Lake Boudreaux bounded by Houma Navigation Canal, Bay Long, Bay Lucien and Bayou Terrebonne. East Terrebonne coastal zone between Bayou Blue Ridge and Bayou Lafourche Ridge including Bayou Barre, Lake Barre, Bayou Jean La Croix, Lake Felicity and Bayou Blue, Lake Raccourei and Timbalier Bay and adjacent coastal waters. Source: URS/Forrest and Cotton, Inc. (1979) page 2. 82 TAELE 6.3 Terrebonne Basin Major Rivers Nam Length in Miles (approximate) Bayou Grosse Tete 30 Choctaw Bayou 10 Grand River 25 Belle River 10 Bayou Blue 20 Bayou Grand Coteau N.D.A. Bayou Lafourche 100 Bayou Carencro 25 Bayou du Large 25 Bayou Black 30 Bayou Grand Caillou 25 Bayou Petit Caillou 30 Bayou Terrebonne 45 Grand Bayou 20 Bayou Penchant 25 Source: URS/Forrest and Cotton, Inc. (1979) page 14. 83 TABLE 6.4 Terrebonne Basin Major Lakes Name Surface Area (Sq. Miles) False River Lake 4.6 Lake Natchez - Lake Verrett 22 Grassy Lake 1.6 Lake Palourde 18 Lake Bayou Black - Lake Fields 3.3 Long Lake 1.3 Lake Cocodrie 0.7 Lake Hackberry 1.9 Lake Hatch 0.3 Lake Theriot 2.2 Lake de Cade 7.6 Carencro -- Lost Lake 6.5 Lake Mechant 13.4 Fourleague Bay -- Lake Penchant 1.3 Caillou Lake - Lake Boudreaux 6.7 Lake Pelto --- Carrion Crow Lake 1.3 Dog Lake 1.3 Fiddlers Lake 0.92 Lake Gero 0.8 Mud Lake 2.2 Lake Pagie 0.90 Lake Tanbour - Catfish Lake 2.4 Lake Felicity -- Lake Barre -- Lake Raccourci 6.5 Little Lake - Old Lady Lake - Wonder Lake 0.92 Source: LM/Forrest and Cotton, Inc., (1979) page 15. 84 Salinities in the coastal region range from that of sea water, through brackish, to fresh. 'Ihese conditions result from freshwater flowing from the north, meting saltwater. Streams may or may not be stratified and my vary with time from fresh to very salty at a single location. Groundwater Freshwater aquifers within the Terrebonne Basin originate from Quaternary, Pliocene and Miocene deposits. Of these water bearing deposits, the Miocene a-re the deepest (up to 3,500 feet below sea level) while the Quaternary are the shallowest (up to 1,000 feet below sea level). Deposits within the Miocene and Pliocene(MioPliocene) zones make up the Mio-Pliocene aquifer. Sands within this aquifer are uniformly graded with coefficients of permability generally within the range of 250 to 1,000 gallons per minute, per square foot. Variation in sand thickness and continuity result in a wide range for coefficients of transmissibility (usually between 100,000 to 300,000 gallons per minute, per square foot). Well yeilds as high as 1,000 to 3,000 gallons per minute are possible in most areas, with even higher well yields possible where screening of all or nearly all available sands is implemented. Water in the Mio-Pliocene aquifer is generally soft. Dissolved solids content (associated with sodium chloride) increase southward where saltwater intrusion becoms significant. 85 Aquifers associated with the Quaternary deposits include the Pleis- tocene aquifer and the Mississippi River Valley Alluvial aquifer. The Pleistocene aquifer overlies the Mio-Pliocene deposits and consists of poorly sorted sands ranging from fine to coarse and graveliferous. Sand thicknesses vary, permability is limited and coefficients of transmis- sibility are generally less than 200,000 gallons per minute, per square foot. Well yields are low to moderate. Water is generally soft and low in dissolved solids content, except in the southern downdip where salt- water intrusion may be significant. The Mississippi River Valley Alluvial aquifer is contiguous with the Pleistocene aquifer and also in hydraulic contact with the Mississippi River. The very fine sand to gravel deposits are highly variable in thickness and range from less than 50 feet to more than 250 feet. Coefficients of permeability range fran less than 500 to more than 3,000 gallons per minute per square foot, and coefficients of transmissibility extend from 40,000 to about 600,000 gallons per minute per square foot. The aquifer possesses the greatest potential for further developmnt with well yields as high as 6,000 gallons per minute. Water is gener- ally hard and high in iron content. Large quantities of groundwater are available thmughout the basin for both industrial and domestic use. The use of this groundwater, how- ever, is significantly affected by its quality, which varies greatly because of vast amunts of brackish and saline waters within the basin. In general, aquifers frcm Quaternary, Pliocene and Miocene deposits north of the 30o latitude have no major groundwater problen-s and conmnly yield more than 1,000 gallons per minute of fresh water suitable for 86 domestic use. Heavy industrial withdrawals in the Baton Rouge area, however, have resulted in a decline of water levels by 100 to 200 feet or more in the West Baton Rouge and southeastern Pointe Coupee parishes and have increased the potential of contamination from saltwater en- croachment. South of the 30P latitude, groundwater sources are found in Quaternary deposits alone and range from brackish to saline. Much of this water is suitable for little else but industrial cooling. Suffi- cient quantities of fresh groundwater for domestic and industrial use are difficult to obtain with the exception of isolated layers or lenses from which pumping must ca-refully be controlled to prevent saltwater encroachment. The portions of the Terrebonne Basin within the South Central District fall into this category (see Table 6.7 for water usage in the South Central District). Basin Description Source: URS Forest and Cotton, Inc (1979). 87 Barataria Basin Basin Description Basin Boundaxies The Barataria Bay Basin is bounded on the west by Bayou Lafourche, on the north by the Lower Mississippi River Basin, on the east by the Lower Mississippi River Basin and on the south by the Gulf of Mexico. Figure 6.1 shows a statewide vicinity map as well as the basin map. There are no parishes that lie entirely within the basin boundaries. `Ihe basin is corrprised of land areas from Plaquemines, Jefferson, St. Charles, Orleans, St. John the Baptist, St. James, Ascension, Assmption and Lafourche Parishes. In general, the basin extends from latitude 30o - 10' N to 28o 551 N and from longitude 910 - 00' W to 890 - 451 W. Basin Hydrology 'Ihe dominant bodies of water in the basin are Lac Des Allemands, Lakes Cataouatche and Salvador, and Barataria and Caminada Bays. A majority of the basin is traversed by numerous bayous, canals and chan- nels. The hydrology of the basin is greatly effected by the fact that the elevation of most of the land in this basin is at, just below or just above sea level. The tidal influence from the Gulf of Mexico is evident as far north as Bayou Des Allemands at the town of Des Allemands. Lac Des Allemands is a large lake about twenty-three square miles of surface area located in the northern paxt of the basin. A large area of swamp land is drained by several bayous including Grand Bayou and Bayou Chevreuil that flow into this lake. Lac Des Allemands is drained to the southeast by Bayou Des Allemands which runs to Lake Salvador. Lac Des Allemands is shallow throughout, averaging about five feet. 88 Lakes Cataouatche and Salvador axe located about ten miles southwest of New Orleans. The lakes are, for all practica1purposes, one body of water being sepaxated only by Gouba Island. `Ihe lakes are fed by numrous bayous, including the large Bayou Des Allemands which enter the northwest corner of Lake Salvador, and drain into the Gulf of Mexico through Little Lake and Barataria Bay. `Ihe surface axea of Lakes Cataouatche and Salvador is 84.5 square miles. Both axe shallow, averaging about five feet. Water quality is quite variable due to the influx of brackish water frcin the Gulf of Mexico during high tides and fresh water during periods of high runoff. Both lakes are brackish at times and the water sometimes exceeds the chloride concentration reconmended for domstic usage. Due to the shallowness and industrial boat traffic connected with oil fields in Lake Salvador, the lakes are usually muddy... `Ihe Intracoastal Waterway crosses Barataria Basin just south of Lake Salvador. It is connected to the Mississippi River on the east by Algiers and the Harvey locks and to Bayou Lafourche on the west by the lock at Larose. A significant amunt of fresh water enters the basins through these locks since both the Mississippi River and Bayou Lafourche have higher water surface elevations than.the Intracoastal Canal. The waters south of the Intracoastal Canal axe estuarine in nature. Barataria Bay is connected to the Gulf of Mexico by Barataria Pass, Quatre Bayoux Pass and Abel Pass, and Caminada Bay is connected to the Gulf of Caminada Pass. These bays are connected to Little Lake and the Intra- coastal Canal by several waterways including Bayou Perot and Bayou Baxataria. 89 Groundwater Groundwater in the Barataria Basin is generally derived in large quantities from strata that is chiefly sand and gravel interbedded with clay. Laxge groundwater supplies axe obtained from alluvial gravels. Saltwater intrusion into the coastal aquifers can be a problem during excessive pumping and/or high tides. Most of the water quality is such that there is little or no potential use for nunicipal water supplies (see Table 6.7 for groundwater usage in this basin). Basin Description Source: Water Resource Engineers (1979). Lower Mississippi Basin Physical Description Basin Boundary The Lower Mississippi River Basin, below the Old River control structure, is bound on the north by the Mississippi state line, on the east by the Lake Pontchartrain Basin and the levee crest; and on the west and south by the crest of the levee of the Mississippi River from the Mississippi state line to Donaldsonville, Louisiana, as shown in Figure 6.1. From Donaldsonville, Louisiana to the mouth of the river, the basin is bound on the west and south by the levee crest and the Barataxia Bay Basin. The boundary of the lower Mississippi River Basin at its southern end is the Gulf of Mexico. Portions of the following parishes are located within the basin as described in Table 6.5. 90 TAELE 6.5 Parishes In Lower Mississippi Basin Pointe Coupee Iberville St. Charles West Baton Rouge Ascension Jefferson West Feliciana St. Janles Orleans East Baton Rouge St. John the Baptist Plaquemines The Mississippi River drains over forty (40) percent of the conti- nental United States. The major tributaries are shown in Table 6.6. TAELE 6.6 Mississippi River Drainage Basin: Major Tributaries Tributary Drainage Area Average Discharge Unit Discharge (square miles) (cfs) (cfs/sq. miles) Missouri R 529,000 70,100 0.13 Ohio R 203,900 255,000 1.25 Arkansas R 160,500 45,200 0.28 Red R 91,400 57,300 0.63 Source: Stanley Consultants (1979) pages 21, 24. 91 A history of disastrous floods and the projection that the Lower Mississippi River would change its course provided the impetus for con- struction of an extensive canplex of levees, control structures, and floodways which regulate the high and low flows. The structures limit flow fran the Mississippi River entering Old River, a branch channel at river mile 314.7, except under flood conditions and provide distributaries, namely the Atchafalaya Basin I'loodway and Bonnet Carre Spillway, or flood waters. Under normal river flow conditions the control structures of the Morganza Floodway, the West Atchafalaya Floodway, and the Bonnet Carre Spillway remain closed. The control structure at Old River, which -is located between Vicksburg (RM 435) and Target Landing (RM 306.6), diverts approximately twenty-five percent of the water frcxn the main stem. The actual percentage diverted is dependent on discharges and stages in both the Mississippi River and the Red River-Old River Corrplex. Under design flood conditions of a dischaxge of 2,720,000 cubic feet per second at Vicksburg and 350,000 cubic feet per second in the Red River, the distributaries and main stEm of the river have the following capacities (which effectively provide the upper limit for maximun flow in the Lower Mississippi River): Old River 620, 000 efs West Atchafalaya Floodway 250,000 efs Atchafa.laya River 680,000 efs Morganza Floodway 600,000 cfs Atchafalaya Basin Floodway 1,500,000 cfs Mississippi River between the Nbrganza Floodway and the Bonnet Carre Spillway 1,500,000 cfs *Bonnet Carre Spillway 250,000 efs Mississippi River below Bonnet Carre Spillway 1,250,000 efs Located in SCP&DC District. 92 in the Lower Mississippi Basin, levees prevent flow fran entering the river from both sides of the river except for an area of 855 square miles drained by Tunica Bayou, Bayou Sara, 'Ihompson Creek, and Bayou Baton Rouge. The streams in this area are of rather low flow contributing less than 0.1 percent of the flow of the Mississippi River. The Bonnet Carre Spill-way is one of only two sources of Mississippi River water entering the district. The other is accomplished by artificial pumping of Mississippi River water into Bayou Lafourche at Donaldsonville for water supplies along the Bayou (see Table 6.7 for water usage in this basin). Groundwater Water bearing soils axe located at various depths as deep as 2,000 feet below man sea level. Most aquifers axe connected hydraulically and movement of ground water occurs rapidly within and to some extent amng aquifers. This novement.is primarily horizontal and down dip due to the impermeable nature of the intervening clay layers. Flushing of saline groundwater.up to forty miles down dip of the normal inland intrusion is one example of this novement. Except for local recharge areas fed by the rising and falling of the Mississipi River stages, all recharge and good groundwater areas are located outside the South Central Planning and Development Comnission District boundaries in this basin. Basin Description Source: Stanley Consultants, Inc. (1979). 93 TABLE 6.7 PUMPAGE OF WATER IN SOUDI CEN71RAL LJOUISIANA BY PARISH, SOURCE, AND PRINCIPAL USE, 1975 (IN MILLIONS OF GALLONS PER DAY) "LIC SUPPLY INDUSTRIAL, 711EMIOLLECTRIC RURA L IRRIGATION IWAL USE PARISH D OMESTI LIVESTOCK RICE 0111ER GROUND G SURFACE GROUND GROUND ISURFACE GnCUND SURFACE GROUND SURFACE GR( VVAL SURFACE Gla-W-1 ASSUMPTION 0 1.55 8.26 10.1 0 0 .02 0 .01 0 0 0 1.34 8.28 13.00 21.28 IARXJlufpl 0 7.63 0 29.0 0 0 0 .04 .18 0 0 0 .03 .04 36.84 36.88 ST. alAlUT'S 0 5.00 11.0 604. 0 1,540 .06 .04 .04 0 0 0 .30 11.10 2,149.34 2,)60.44 sr. imu 0 1.66 5.15 275. 0 0 .04' .02 0 0 0 .11 7.91 5.32 284.57 289.99 ST. JOHN 'IIIE BAPTIST 1.03 1.37 3.88 87.7 0 0 .05 .01 .01 0 0 0 .35 4.97 89.43 94.40 IETWU14NE' 0 17.0 .54 3.36 0 0 0 0 .05 0 0 0 .09 .54 20.50 21.04 SOURCE: Louisiana Lbpartrmnt of Transportation and Develolvient (1.979): 14-15 BIELIOGRAPHY Cardwell, G. T., and Walter, W. H. (1979) Special Report No. 2: PLvnpage of Water in Louisiana, 1975. Louisiana Departmnt of T@ransportation and Development, Office of Public Works in Conjunction with the United States Geological Survey, Baton Rouge, Louisiana. Stanley Consultants (1979),Lake Pontchartrain Basin Water Quality. Management Plan Draft Final Report. Louisiana Stream Control Gonnission, Department of Wildlife and Fisheries, Baton Rouge, Louisiana. Stanley Consultants (1979),Upper and Lower Mississippi Basin Water Quality Managemnt Plan Draft Final Report. Louisiana Stream Control Comission, Department of Wildlife and Fisheries, Baton Rouge, Louisiana. URS/Forrest and Cotten (1979) Terrebonne Basin Water Quality Managerwnt Plan Draft Final Report. Louisiana Stream Gontrol Comnission, Departmnt of Wildife and Fisheries, Baton Rouge, Louisiana. Water Resource Engineers (1979) Barataria Basin Water Quality Managemnt Plan Draft Final Report. Louisiana Marine Control Corrmission, Departmnt of Wildlife and Fisheries, Baton Rouge, Louisiana. 95 CHAPTER 7 - THE WETLANDS ECOSY= By Edwin J. Durabb INTRODUCTION The South Central Planning and Developmnt District land area sits astride one of the most dynamic and productive ecosystem in the world. In its entirety, coastal Louisiana contains about 102-1, million acres of land: 1-21 million acres axe dry land, and &12- million are coastal wetlands. These 821 million acres represent roughly 25 percent of the entire wetlands average in the United States (Louisiana State Planning Office, 1977). South Central Planning and Development Coninission contains nearly 31 percent (or 3'ff million acres) of the State Total Wetland Area (Louisiana State Planning Office, 1975). In previous chapters the geology, climate geomorphology, vegetation, water drainage and soils of the South Central Region have been discussed. These elements make up the parameters that enable the estuarine ecosystem of wetlands to function as a productive system to man and nature. The following is a discussion of the workings of this system and its value to man and to nature. The wetlands estuarine ecosystems of,coastal Louisiana are excellent examples of a productive, circular biologic system. The primary elements in this system are: 1. Sediinent 2. Wetlands 3. Detritus 4. Water 5. Living Organism 6. Other Properties of Ecosystem. 96 Each of these elements operate singly and in concert with the others to produce the massive biologic productivity of the coastal areas of our state. The following is a discussion of each element of this system. SEDIMENr Sediment perform several functions in the wetlands ecosystem: 1. Provides the base material upon which the ecosystem exists. 2. Shapes the surrounding landforms to delineate the estuarine. basins. 3. Provide nutrients necessary for plant growth. Before the advent of man, yearly overflow of the Mississippi River on its deltaic plain provided the sediment load responsible for deltaic plain progradation. Deposition within estuarine basins was limited to fine clays, heavier silty materials being deposited on the "natural levees". Since the advent of man and artificial flood control structures almost all sediment deposits have ceased within the South Central District (see Part I, Chapter 2 for a discussion of natural levees and deposition). WETLANDS The wetlands areas, consisting of swamp forest, fresh, brackish, and saline marsh, provide the floral vegetation component of the ecosys- tem. This vegetation provides habitat and food for primary consu-ners and provides I'detritus" to the estuarine system (see Chapter 5 for a discussion of vegetation). 97 DEMITUS "Detritus" or partially decomposed organic matter can be com@- pared to the fuel that powers the living estuarine ecosystems in each basin. This material, derived from plants and animal waste, forms the food source for the organisms that make up the base of the wetlands food chain. WATER Water is the integrating factor in the estuarine ecosystem of the South Central District. Water performs the following functions: 1. Transports sediment from the River into wetlands areas pro- viding nutrients to the basin. 2. Transports detritus throughout the system, providing the basic food source for the food chain base. 3. Determines the vegetation type at any point in the basin by its depth and salinity. 4. Provides the livingenvironment directly or indirectly for all of the creatures of the ecosystem. 5. Provides the mans of travel for the interaction of the living creatures of the system. LIVING ORGANISMS These are the creatures that use the natural resources of the system in their life cycles and generate the plethora of life both qualitatively and quantitatively, that exists in the ecosystem. 98 OTHER PRCPERTIES OF ESTUARIES Table 7.1 lists other properties of estuaries that interact to form the ecosystems extant in the South Centra.1 Region. These elements involve water, landforms, vegetation and detritus. These driving forces keep the system operating at a peak level of productivity. 99 TAELE 7. 1 Physical Properties Governing Productivity of Estuarine Systems 1. Cc)nfinement a. provides shelter that protects estuary from wave action b. allows plants to root C. permits retention of suspended life and nutrients 2. Depth a. allows light to penetrate to plants on the bottom b. fosters growth of marsh plants and tideflat biota C. discourages oceanic predators which avoid shallow water 3. Salinity a. freshwater flow may create a distinct surface layer over saltier, heavier bottom layer, indicating beneficial strati- fied flow: b. fresh water dilution deters oceanic predators and encourages estuarine form 4. Circulation a. sets up beenficial system of transport for suspended life when stratified such that the bottom layer flows in and the surface layer flows out b. enhances flushing C. retains organisms in favorable habitats through behavioral adaptations 5. Tide Driving Force a. transports nutrients and suspended life b. dilutes and flushes wastes C. acts as an important regulator of feeding, breeding, etc. 6. Nutrient Storage a. trapping mechanisms store nutrients within the estuary, b. marsh and grass beds store nutrients for slow release as detritus C. richness induces high accunulation of available nutrients in animal tissue Source: Clark, 1974: 2. 100 A VIEW OF TBE ECOSYSM OF THE ESTUARINE BASIN In this section we will travel down the estuarine system from the upper portion of the basin to the sea to provide the reader with an insight into the complex system at vurk in the wetlands axeas that com@- prise the coastal areas. This section draws heavily from the-work of Clark (1974), MmVhrey et al (1975), Day et al (1972), and Bahr and Hebrard (1976) for information on the ecosystem function. Let us begin our journey. Upper Basin Freshwater enters the system through river overflow and rainfall. This water is fresh and laden with sediment and nutrients as it flows off of the natural levee into the swan-p forest. Trees living here use sunlight and these nutrients to grow. The shed organic matter into the shallow water is used by the organi,@=zrs there as well as reused by the aquatic and terrestrial plants growing in the area. Three primary organi-cam operate here and throughout the rest of the system to form the base of the food chain. Although the location within the estuary will determine the species of animals present, their function in the system is the same (Day et al, 1973, and Mamphrey et al, 1975) have determined their function thusly: Packagers organize organic material into fo= available for convenient transfer to higher tropic levels (life requiring higher forms of nutrition). These packagers may be autotrophs (they make their own food) or heterotrophs (they consuDee primaxy plant matter). Cord grass (Spartina) and phytoplankton axe examples of the fomieer; snails and zooplankton are examples of the latter. 101 Regulators are organisms with generalized feeding habits. They regulate populations by feeding on the most abundant food sources. Regulators have longer life spans and larger individual sizes than packagers. They are also highly mobile. Regulators axe sub divided into two classes: subsystem regu lators and whole system regulators. Subsystem regulators feed on specific organism, thus controlling specific populations. Catfish, blue crabs, shore birds, drum, croaker, etc. are considered subsystem regulators. This level (subsystem regulators) is analogous to mid-level carnivores. Whole system regulators feed on system regulators, as well as what the subsystem regulators feed on. Thus, they regulate the other regulators. 'Ihis group includes animals such as trout, coons, wst birds, and man. There is little predation on these organisms (also called top carnivores), except by man who, of course, has assumed the role of regulator of the entire system. 'Ihe Regenerators take waste from all sources and regenerate these wastes into nutrients to staxt the whole cycle over again. Bacteria, yeasts, etc., are examples of this type of organism. Table 7.2 illustrates some exanples of each type of organism. It is by no means implied that these categories of life are rigid. There are organisms that function in mre than one capacity. What these categories attempt to do, is point out the organism's primary function in the estuary. This enables the larger scheme of life to be assembled more siraply to give the reader a more general, but fairly accurate view of the circle of life. Source: Mwphrey et al (1975), pages 45, 47. 102 TABLE 7.2 Ecological Roles of Some Estuarine Species Packagers Regulators Regenerators Spartina Mature Fish Bacteria Benthic Algae Proposus Yeasts Periphyton Pelicans Molds Phytoplankton Herons Meiofouna Killifish Egrets Protozoa Shrirrp Gulls Fiddler Crabs Carb-jellies Juvenile Fish Raccoon Marsh Snails Man Modiolus Oysters Source: Day et al, 1973. 103 rilie Swamp Forest provides habitat for birds, fish, reptiles, insects, etc. Water flowing by mans of pressure and a very slight downhill grade moves detritus and organism out of the swamp forest into the fresh marsh. Presh Marsh Fresh water continues its flow to the sea through the fresh marsh zone. Two kinds of flow occur throughout the ecosystem sheetflow and channel flow. Sheetflow is the general movement of surface water through the wetlands towards the Gulf. This is important because this slow flow allows nutrient exchange between the marsh and water. Detritus is used and new detritus is produced and moved downstream. Channel flow is also slow but here the water is slightly deeper and moves a bit faster. Ade- quate nutrient exchange occurs here also. The only effect the Gulf of Mexico has on freshwater areas is a very slight tidal influence. Habitat is diverse here. A few mre species of marine fish have been sighted near the lower end of the freshwater area, but, for the most part, this zone is noted for the detritus and fresh water it supplies to the lower part of the basin, as well as for habitat. Brackish Ma-rsh This zone may be the most important part of the estuary system. It is here that inland fresh water and fresh water species met marine waters and their associated organisms. In this zone, tidal influence is more pronounced and the water tends toward increasing salinity. Many species of sea animals use this zone for nursery areas. Among them are menhaden, shrimp, crabs, and others. 104 Perret (1971) has estimated that the estuary is relied on directly, (nursery and habital) or indirectly (food sources), by seventy-five percent of all fish and ninety percent of the eight most abundant fish and invertebrates that inhabit Louisiana's coastal waters. It is in the brackish water zone that juvenile sea creatures feed and are protected until they can fend for themselves in open water. The prime reason for this brackish water zone is the shallow sinuous channel flow to and from the Gulf, as well as sheetflow. In these shallow, slow moving systems, water tends to mix rather than maintain its saline or fresh integrity, thus modifying extremes to a great extent (Clark, 1974). This single fact has enabled this zone to serve as the nursery area of the estuarine system. It is also here that man-made influences have upset the balance of the ecosystem the most (see Part III, Chapter 4 for further discussion). Salt Marsh This zone is highly marine in character. Detritus and fresher waters intrude occasionally, but saltwater is the norm for this a-rea. Although not as productive as the brackish zone, this area serves similar function. Daily tidal flushing is high here, and this area is subject to rapid erosion during storm periods. As this area erodes, each zone is pushed further inland. This is a natural process that eventually results in the sea reclaiming the entire deltaic plain. Here, as elsewhere, man-made influences have altered the ecosystem significantly and increased the rate of erosion. 105 Resultant Estuarine Productivity The result of this estuarine interaction within these coastal basins (Pontchartrain, lower Mississippi, Terrebonne, and Barataria) is tremendous productivity. It is no accident that the state with the most wetland area also leads the nation in fisheries production. Tables 7.3 and 7.4 illustrate is productivity in the area of conmrcial fisheries. These figures do not include the sport fishing catch in Louisiana waters. The millions of birds, especially ducks that frequent the marsh and the fur bearing creatures that are harvested yeaxly, also enhance the value of this ecosystem to man. Table 7.5 lists some of the benefits that the coastal wetlands provide to man and to nature. Later in this report, we will investigate what man has done to this ecosystem and the effects of these activities on the evolution of the wetlands. 106 TABLE 7.3 U. S. OOMMERCIAL LANDINGS* U. S. Commercial Landings, By States'. 1975 and 1976 (1)(2) (Six Leading States) 1975 1976 Record STATE Landings Thousand Thousand Thousand Thousand Year Thousand Pounds Dollars Pounds Dollars Pounds Louisiana 1,124,586 88,245 1,227,958 136,971 1971 1,401,252 California 850,000 129,366 896,858 185,647 193.6 1,760,183 Virginia 444,110 32,463 528,430 43,091 1972 666,180 Alaska 437,908 143,836 616,351 227,208 1936 932,341 Mississippi 308,502 15,520 291,904 22,006 1971 400,576 Massachusetts 269,952 78,470 288,518 97,605 1948 649,696 (1) Statistics on landings are shown in round (live) weight for all item except univalve and bivalve mollusks such as clams, oysters, and scallops which are shown in weight of mats excluding the shell. (2) Landings in interior waters estimated. * Ranked by weight of catch. Source: U. S. Department of Cofffkerce (1977) page 4. TAELE 7.4 U. S. COMMERCIAL LANDINGS Quantity of Commercial Fishery Landings at Certain U. S. Ports, 1976 Port Thousand Pounds San Pedro, California 600,900 Cameron, Louisiana 385,300 *Dulac-Chauvin Louisiana 236,900 Pascagoula-Moss Point, Mississippi 218,600 Empire, Louisiana 214,000 Morgan City, Louisiana 163,800 Kodiak, Alaska 151,400 Gloucester, Massachusetts 144,200 San Diego, California 100,700 Dutch Harbor, Alaska 91,300 Located in SC2D&DC District Source: U. S. Department of Conmerce (1977), page 5. 108 TA12LE 7. 5 Benefits of the Estuarine Ecosystem A. Benefits to the Natural System 1. Habitat for birds, fish, mam-nals, reptiles and the vaxied flora of the region. 2. Nursery area for birds, fish, mamnals, and reptiles. 3. Food Source for the creatures of the open Gulf of Mexico. 4. Nutrient source for luxurious plant growth of the basins. B. Benefits to Man 1. High assimilative capacity to absorb pollutants. 2. High yield of birds, fish, maninals, reptiles to both comnercial and sport interests. 3. Buffer zone against tropical storms. 4. Recreation area for coastal residents. Source: Author 109 BIELIOGRAPHY Bahr, L. M., and Hebrard, J. J. (1976) Barataria Basin: Biological Characterization. Center for Wetlands Resources, Louisiana State University, Baton Rouge, Louisiana. Clark, J. (1974) Coastal Ecosystem : Ecological Considerations for Managemnt of the Coastal Zone. The Conservation Foundation, Washington, D. C. Day, J. et al (1973) Community Structure and Carbon Budget of a Salt Mai:@-h- -@x-id Shallow Basin Estuarine System in Louisiana. Center for Wetland Resource, Louisiana State University, Baton Rouge, Louisiana. Louisiana State Planning Office (1977) Louisiana Coastal Resources. Louisiana State Planning Office, Baton Rouge, Louisiana. M:umphrey, A. J. et al (1975) Louisiana Metropolitan Wetlands: A Planning PJ-s@@tive. I an Studies Institute, University of New Orleans, New Orleans, Louisiana. (Unpublished) Perret, W. S., et al (1971) Cooperative Gulf of Mexico Estuarine Inventory @iTd-Study, Louisiana: Plause I and IV. Louisiana Wildlife and Fisheries ConTnission, New Orleans, Louisiana. National Marine Fisheries Service, National Oceanic and Atmospheric Administration, U. S. Departmnt of Commerce (1977) Fisheries of the United States 1976. U. S. Government Printing Office, Washington, D. C. 110 - -Y @ PART LAND USE CHAPTER I - PCPULATION AND SEME= PATTMNS By Dr. Paul Leslie GENERAL HISTORY At the end of the seventeenth century when initial European contacts with Louisiana occurred, about 15,000 Indians lived in the state (Davis, 1965). There were numerous tribal groupings, but in the Lower Missis- sippi Delta were about twelve different tribes, only five of which lived permanently in the South Central Planning District. They included the Chitmacha, on the upper portions of Bayou Lafourche; Washa/Chawasha, in the middle portions of Bayou Lafourche; Quinipissa, near present-day Hahnville; Bayougoula, on the Mississippi River south of Baton Rouge; and Tangipahoa, along the north and south shores of Lake Pontchartrain (Knipmeyer, 1956). The tribes of the area belonged to the Eastern Maize Culture group, hunters and fishermen who depended on agriculture for their foodstuffs. For most Indians agriculture dominated their daily routines. The tribes first cleared their fields by tree deadening or burning. Then, to break the land, they used makeshift implements. Every so often these plots lost their productivity and forced the tribes to shift their crop pro- duction to adjacent lands. All of these tribes lived in rectangular structures with wattledaubed walls and palmetto roofs, or houses made entirely of palmetto; these structures were arranged adjacent to a cen- tral area that the tribe used in common (Davis, 1965). ill The French were the first to make colonization efforts in Louisiana. In 1718 they successfully founded a colony at what muld later becom New Orleans, an inTporiant support facility for further colonization along the Mississippi and inland waterways. Prior to 1718, the French govern- ment had unsuccessfully tried to settle the Mississippi. Its frustra- tions ran so deep that for many years governmient officials limited their activities to the area along the Gulf coastal region (Taylor, 1976). Under the French, the colony did not experience rapid growth. In 1721 there were 370 residents in New Orleans, and by 1770 only 3,190 (Davis, 1965). Colonists did not realize their initial expectations; trade with the Indians and Canada never reached anticipated levels. The settlers were disinterested in farming and frequently ccmplained about the"sterility@'of the soil. They had come for quick riches, but colonizers found swampy lowlands, disease, tropical storms, occasional Indian hostilities - and no precious stones (Taylor, 1976). For the most part, the French settlers stayed near New Orleans. The first large-scale settlement movement beyond the boundaries of the Crescent City cam during the 1720s when John Law took charge of French colonization efforts; for the government now gave more attention to increasing the numbers of settlements in Louisiana. Government agents con-bed the European countryside trying to infect all who mould listen with colonization fever. Their efforts attracted large numhers of Germans, who eventually cam to Louisiana to establish farm and raise families but not to make quick riches. 'Iheir decision to come to Louisiana, according to one observer, "probably saved the colony," (Davis, 1965). 112 The Germans proved to be excellent pioneers. But even before coming to the new world they faced tremendous hardships. Officials forced thousands to wait in French ports before they could book passage. When almost 6,000 left, they were forced to wait again in Gulf coastal ports while administrators pondered their fate once again. Detention took its toll, because one estimate is that only 2,000 out of the 6,000 ever reached Louisiana. Still, once the Germans gained access to their lands, they went to work and helped the colony lessen its dependence on outside foodstuffs. Interestingly, the German settlements were never large. For example, the town of Hahnville, which had begun to show the early signs of settle- ment activity, had 167 residents in 1724, but only 174 in 1731. Me reason is that the French began discouraging German migration. A5eanwhile Germans already in the colony were quickly gallicized by their neighbors. The cultural uniqueness of the Germans disappeared and so did their Teutonic names; Trisch became Triche and Foltz became Fol.se (Taylor, 1976). Few Germans went into the marsh to trap and fish; instead, they cultivated the lands above New Orleans where their settlements acquired their own distinctiveness. This area became known as La Cote des Allemands. Later these settlements were divided into Primera Costa (St. Charles Parish) and Segunda Costa (St. John the Baptist Parish). And west of New Orleans, such place names as Lake Des Allemands and Bayou Des Allemands still provide evidence of these earlier settlers (Knipmeyer, 1956). 113 The French were never successful in sustaining the growth of the colony. Only after 1762 when Spain took control of the colony from France as a settlement for the French and Indian War did Louisiana's population begin to grow. In New Orleans, for instance, the population increased from 3,190 in 1770 to 10,000 by 1803. The Spanish were very interested in putting as many new colonists as they could between their colony and the Anglo-Americans, and one of their chief inducements was free land. Spanish authorities promised each settler five axpents of land (192 feet per arpent) fronting a waterway and approximately forty arpents deep Each family also received a spade, two hens, a cock, and a two-month old pig to establish a household. The only government Urposed conditions were that the imadgrants swear allegiance to Spain and openly practice the Catholic religion (Davis, 1965). The primary beneficiaries of the Spanish policy were the Acadians, who arrived in Louisiana during the 1760s after having been driven out of Nova Scotia (Acadia) by the British during King George's War. Thousands fled to Canada and to the Atlantic seaboard. The largest group (4,000 to 10,000) came to Louisiana where they were accepted by the people who were culturally related. The Acadians first settled near modern-day St. Martinville, but later groups went up the Mississippi and down Bayou Lafourche to establish the Acadian coasts. For the most part, these simple people, sometinies called petits habitants, were excellent small farmers. They tended to isolate themselves from the rest of the colony and asked others to respect their separate society. Over the years, the Acadians multiplied so much so that in 1772, Spa-in 114 created the ecclesiastical Parish of Ascension. Six years later, in 1778, the district of Valenzuela was established in what today is called Assumption Parish. The Acadians followed a fairly routine existence on Bayou Lafourche. Once on their lands, they unpacked their cultural baggage and tried to reconstruct the familiar sights, smlls and sounds they had known in Canada. They built simple cabins and cleared and tilled the soil with the help of their families. Generally, there were no large landholders, each family having only what it needed to survive. They relied on such standby crops as corn and rice and learned to grow new ones, such as cotton and possibly okra, and African vegetable. Cattle and other domestic animals were left to roam unattended at the swamp's edge. And for those needs beyond the farm, these petits habitants cut and marketed swamp cypress and Spanish mss (Voorhies,.1978).. Some Acadians turned away from subsistence agriculture and engaged instead in hunting, trap- ping, fishing or lurbering. But, for the most part, they were small faxmers who raised what they needed to maintain their families. The influx of so many French Acadians caused concern amng Spanish officials that their control of the new colony would be undermined. To offset this they recruited Spaniards from the Canary Islands and the Iberian Peninsula. Called Islenos, they established themelves on the eastern bank of the Mississippi, below New Orleans, and at Valenzuela in Assumption Parish. Ethnographically, however, the Islenos fared no better than the Germans; only a few place names and family surnames (Martinez) have survived (Knipneeyer, 1956). 115 One group that Spain did not have to spend time or money recruiting to its colony was the Anglo-American who began to arrive in large nuThers after the Revolution. They came by land and sea fran all the states seeking the free land that Spain offered to new settlers. These newcomers scattered all over the state, establishing commercial shops in cities and establishing plantations along the waterways. The arrival of the Anglo-Americans was felt especially along Bayou Lafourche as the Acadians attempted to recreate their former Canadian lifestyle. But with the crystallization of sugar by Etienne de Bore in 1974, cotton planters and mall farmers from the lower South beseiged South Louisiana, hoping to get ahead. As the accompanying population tables indicate, the boom and bust cycles of cotton caused many newcomers to turn to suga-r as an alternative. With its fertile natural levees and a waterway linking the Mississippi River with the Gulf of Mexico, Bayou Lafourche and its adjacent waterways became the center of resettlement activities. In 1827, no less than $50,000 mrth of its woodlands were purchased by planters from the Natchez, Mississippi area (Sitterson, 1953). Each week, one New Orleans newspaper noted, saw the arrival on the Bayou of prospective purchasers "to examine the country with the view of purchasing and settling therein," (Sitterson, 1953). For the Acadians the offers were indeed tempting. Many sold their lands. Thus an area once densely settled by French-speaking white yeoman farmers was soon transformed into plantations occupied by a few wealthy Americans with mny black slaves (Comeaux, 1978). 116 From the beginning, African slaves had been imported into the colony. Their numbers, however, were never large. They constituted less than twenty percent of the colony's population and the rapid in- crease in their numbers cam only after the invention of the cotton gin and the crystallization of sugar. Along Louisiana's waterways planta- tions developed, their vork force being black bondsmen. 'Ihe plantation economy depended on African laborers so much that just before the Civil War blacks in agricultural parishes represented more than fifty percent of the total population. After the war, the black population began to decline because of econcmic distress, labor-saving technology and such disasters as floods. By the time of the Louisiana Purchase in 1803, the intermittent waves of immigrants had produced a continuous line of settlement below Donaldsonville. These included the German Coast (St. Charles and a portion of St. John the Baptist Parishes) and the First and Second Acadian Coasts (St. John the Baptist and St. Jams Parishes). In addi- tion, the petits habitants had established Acadian settlements along Bayou Lafourche between Donaldsonville and Thibodaux. SETILEMENT PATDMS Down through the twentieth century, the settlement patterns of the South Central Planning District were dictated by its waterways, the area's primary transportation arteries. Both the French and Spanish bad found waterways a convenient reference point for dividing the land; both governments employed the arpent (192 feet square) as their measuring 117 unit. Land grants were usually five by forty arpents. This system insured that the grantees would receive the different qualities of land evenly. This practice produced long continuous lines of closely spaced buildings on the levees. These structures fronting the waterways constitute what William Knip-neyer called the linear settlEment mode, a pattern characterized by long lines of buildings interrupted at irregular intervals by varying lengths of empty spaces (Ehipmeyer, 1956). Today the linear settlements are held together by roads on either side of the waterway, the automobile having replaced the boat. Within the South Central Planning District, the settlement along Bayou Lafourche represents possibly the clearest example of the linear pattern. For almost one hundred miles below Donaldsonville, there is an almost uninterrupted succession of buildings. Exanples of this mde are the settlements of Bayou Point aux Chenes and Bayou Dularge. Within the linear settlEmnt, however, axe internal distinctions that further set-off the.populations from each other and adjacent lands. The most striking involve urban and agricultural areas. Whether on the Mississippi or Bayou, urban settlEmnts are popula- tion centers developed at the convergencies of waterways, crossings or where early settlers saw fit to erect their church. The location of churches was especially important. Because after them came the construc- tion of commercial buildings and then schools. Some idea of the impor- tance of this factor can be gained along the Mississippi "here churches and urban com=ities appear every twenty or so miles and along Bayou Lafourche where ten miles is the approximate distance of separation (Kniprmyer, 1956). 118 The simple nucleus of a church, school, and commercial activities became the springboard for more complex urban growth. According to Knipmeyer, these linear settlements began to expand into more advanced form, such as the "T" towns and the grid cities. The "T" town has a population of 1,000 to 2,500 and includes at least one street perpendic- ular to a waterway. Also there is an increase in the number of conrercial establishments and services offered by professional (as in Labadieville and Luling). As the "T" town grew, streets paxallel to the waterway were built and generally became the first indication of its transforma- tion into a grid city. In the grid city the population is more than 3,000 and the services provided residents are more varied and numerous. Moreover, in grid cities, such factors as the confluence of roads or waterways are more significant in triggering growth (as in Houma, Napoleonville, and Thibodaux), (Knipmeyer, 1956). Finally, there is the dispersed settlement which is neither urban nor agricultural. It includes the swamp and marsh populations. The swamp population is on the periphery of large swamps, similar to the area between the Mississippi River and Bayou Lafourche, or around Lake Maurepas and Lake Pontchartrain. The houses of these settlements are in an unorganized pattern, generally along the roads or bayous leading into the swamp. The marsh settlement is distinguished by its dependence on trapping. The residents live on lake shores or banks of bayous and canals. Their numbers axe never large since the occupations of the ma.rsh people are seasonal. At present the marsh settlement is in decline as more and more residents seek employment security. These settlements are characterized by large numbers-of single family members and limited inter-relationships with other settlements (as in Bayou Gauche and Isle a Jean Charles near Point =x Chenes), (Knipmi-eyer, 1956). 119 Tables 1.1, 1.2, and 1.3 illustrate the population growth patterns in the South Central District from 1810 to 1970. 120 TABLE 1. 1 TOTAL POPULATION 1810 IRM im 1940 181.0 1960 1870 Mo 1" 1900 19104 IM0 IT" A,3.-*mVtlon 2,472 3,M 5.6m 7,141 10,518 15,17D 13.2.M 17,005 19,616 21,620 24,128 17,012 15,9%. I.M 3,750 5,425 4,425 9.5.12 14,IM4 14,719 19,088 22,0&q 29,882 33,111 10,344 32,419 St. Otarlea 3,291 3.9r,3 5,147 4,700 5,120 5,21YI 4,867 7,147 7,737 9,072 1 t,207 fl,w 12, 11 t St. Jnffea 3, 9.5 7 5,GW 7.010 8,-As 11,0r)a 11,4M. 10.152 14,712 15,ma 20,107 23.OM 21,228 is, 3,V St. NAM tfw- DaptInt 2'" 3,654 5,677 5,776 7,317 7'rm. 6,7M 9.W 11,317 12,330 14,338 11,8.90 14,078 lbrretxmim 2,121 4,410 7.724 11.9m 12,45t 17,72-1 20,111 24,4M 28,320 20,914 2q,816 IrmilsiviiR lbtRI.9 70,5m 153,407 215,739 352,411 517.762 70R,OM 726,915 939,94n 1, 118, 5M 1,381, M,5 1,&96,398 1, 798, RV 2,101,M Distriet Totain (12,M) (18,803) (31,(;&13) (35,000) (51,329) (M. 137) (62. t85) (85,321) (M,518) (114,113) (116.IMO) . (119,7132 Source: U. S. Census Reports, 1810-1970. TABLE 1.2 WHITE POPULATION PARISH 1810 1820 im 1840 18.5 0 1860 1870 1880 1890 low 1910 1920 1930 1940 1950 1960 1970 A.&'31JMI.yl'ION 1,915 2.409 3,760 4,103 5,170 7,189 6,247 8,933 10,726 12,181 14,021 10,425 9,611 11.010 NIA N/A N/A 1,681 2,712 5,025 3,998 5.142 7,500 8, OGO 11,232 14,270 20,626 25. M .24,456 27,037 32,659 36,531 N/A N/A ST. 01AMES 820 728 676 874 867 938 897 1,401 1,986 2,970 4.487 .4,239 7,932 8,412 9,002 N/A N/A ST. JAMPS 1, 964 2,522 2,557 2,762 3.285 3,318 3,275 4,85) 5,691 8,839 9.844 91624 7,742 8. 368 7,626 NIA NIA ST. JOHN 111E Mvrisi' 1, 4(f2 1,402 1.980 2,141 2,586 3.037 2,715 3,853 4,680 5,145 6,208 5,476 7,131 7.890 7,445 NIA N/A NIA NIA 1,063 3,946 3,305 5,131 6,080 8,613 10,412 14,142 16, 0@ 1 17,586 20,431 25,997 32,658 N/A N/A IMISIANA IUMB 34,311 73,383 89,441 158,457 255,491 351,556 N/A N/A 558,395 729,612 94t.086 1,095,611 L,318,160 1,511,739 NIA NIA 1v/A Source: U. S. Census Reports, 1810-1970. TABLE 1.3 BLACK POPULATION rARM, 1 18106 la" 18306 1840* 19506 18690 19704 1980 IACV) 1900 1 q@ 0 lom lqao 1910 1950 Im I Wo &-.-; i vp t t n n 557 1.161 1,9m 3,018 5,368 8,190 6,P91 8, om 8, SIX) fl, 4.% 10.105 7.4R7 6,319 ?. &,N) MIA 141A MIA l'"f0tlrrlw. X" 1'(138 400(7) 427 4,3.w 6.5A4 6, r1ro 7,806 7, 8 19 It, 10 4 7,973 5.898 5,313 4.6,15 5, C178 MIA MIA St. 2,471 3'lm 4.,Vn 3,826 4,253 4, X0 3'ma 5,746 5,751 0, 1 C12 6,720 4,347 4,19.9 1,9(0 4,36t "/A MIA St. 3,1.18 5,089 5,7SA 7,R13 8,151 6,877 9, 862 9, fm i I., W)tj 13,161 it.602 7, @50 S. 228 7,708 MIA MIA St. 30111 tllf- rliptlat i.rm 2,452 3,697 .3, C'15 4,731 4,M 4,044 5,792 6. C01 7,184 8, 12r, 6,415 6.9117 6.876 7,41 F; N/A MIA Ter r(l"ne MIA MIA I'" 4CA 4,419 6,8557 6,172 0,111 U, ow) 10,312 11,191 8,742 8,349 8.8zl 10.070 MIA MIA liwininna n)CnIs MIA MIA MIA MIA MIA (-m5,273) MIA MIA (!' X". IR] (050,")(713,874) (700.257) (770.326) MIA MIA MIA Incitioks Onvo Fx4milation nnd f" HtMnyes. Source: U. S. Census Reports, 1810-1970. BIELIOGRAPHY Comeaux, M. (1978) "Louisiana Acadians: The Environmental Impact" from Voorhies, J. (1978) The Cajuns: Essays on -their History and Culture. University of Southwestern Louisiana Press, Lafayette, Louisiana. Davis, E. A. (1965) Louisiana: A Narrative History. Claitor's Book Store, Baton uge, Louisiana. Knipmeyer, W. B. (1956) Settlement Succession in Eastern French Louisiana. Unpublished Masters Thesis, Louisiana State University, Baton Rouge, Louisiana. Rehder, J. B. (1978) "Diagnostic Landscape Traits of Sugar Planatations In Southern Louisiana" in Geoscience and Man, Vol. XD@. Louisiana State University, Baton uge, Louisiana. Sitterson, J. C. (1954) Sugar Country: The Cane Sugar Industry in the South; 1953-1950. TH University of Kentucky Press, Lexington, Kentucky. Taylor, J. G. (1976) Louisiana: A History. W. W. Norton, New York, New York. U. S. Department of Gonmrce,Bureau of the Census, Number of Inhabitants Louisiana,(1810-1970 Reports). U. S. Government Printing Office, Washington, D. C. Voorhies, J. (1978) "The Search for the Promised Land" fran The Cajuns: Essays on Their History and Culture. University of Southwestern Louisiana Press, Lafayette, Louisiana. 124 CHAPIER 2 - AGRICLUTURE By Dr. Paul Leslie And Edwin J. Durabb HISTORY The agricultural settlements of the South Central District have been a part of the landscape for more than tvu hundred years. Originally, the single family establishment dominated the area's physical environment. But as the number of inhabitants increased and commercialism became a part of agriculture, the large sugar plantations dominated the landscape. Although the family-based agricultural units are easily recognized, the plantation environment exhibits a trait of agglaneration, so that small villages are apparent. The most conmn plantation pattern that developed along the Missis- sippi was the linear settlement. Owners constructed a centralized road through the heart of their land and flanked it with dwellings for laborers. The sugar rrdll and its outbuildings were located at the end of the road and close to the back swamp. In this case, the owners sought to minimize the distance cord mod would have to be hauled. The second pattern of plantation development was that of the block shaped, used most often along Bayou Lafourche. Clusters of what John Rehder called nodal blocks were placed near the center of the land holdings. Connected to the Bayou by a central road, the block surrounded the sugar house with a 125 grid-patterned workers' settlement. The reason for this arrangement is that the front part of the natural levees were originally settled by the Acadians, and the Anglo-Anjericans, upon reaching Bayou Lafourche, found themselves limited to the backlands. At a later date, many American settlers purchased parcels of frontage from the petits habitants (Rehder, 1978). r1he remaining agricultural settlement form developed in Terrebonne Parish. Unlike the buildings in the Mississippi and Bayou Lafourche developments, plantation buildings were located closer to the waterways of Terrebonne and on the crests of the natural levees of both banks. With its western neighbors, Terrebonne Parish was the last of the state's lands opened for settlement and consequentially the lands pur- chased by Anglo-Americans included wide waterway frontage (Rehder, 1978). SUGARCANE After much trial and error the crop of sugarcane was selected as the agricultural conundity best suited to the soil and climate of the natural levee soils in the South Central District. This fact has held true into the twentieth century. In recent years, hov&-ver, with the fluctuating nature of the sugarcane market, the industry has fallen upon hard times. Figure 2.1 illustrates the current status of the industry as of 1979. As can be seen, there has been some economic decline reflected in processing mill closings in the last few years. This crop still, by fax, however, occupied the most available land and employs the most people of any agricultural endeavor in the South Central District. 126 Fact Sheet for Sugarcane Industry within Boundaries of South Central Planning & Development Cannission I Mills A) Number of Mills in area 10 B) Number of Mills in state 28 35.77o of the mills in the state are in this area. Q Three (3) Mills closed in the last three (3) years D) 100 workers (average) are employed by the mill@ during grinding. With 100 workers (average) per mill and 10 mills in the district approximately 1000 workers are r=mployed during grinding. E) Lmiediate Needs of Mills 1) Pollution devices (both water and air) 2) Changing boilers from natural gas as a fuel to baggass. II Faxming of Cane A) Cane Acreage for 1978 Production PARISH ACREAGE Assumption 38,187 Lafourche 34,472 St. Charles 1,638 St. James 23,358 St. John 14,472 Area Total 120,157 State Total 296,000 % 40.6% 127 B) Farms in the Area PARISH NUMBER OF FARMS Assumption 110 Lafourche 126 St. Charles 3 St. James 75 St. John 26 Terrebonne 47 Area Total 387 State Total 1007 % 38.47o C) Average Acreage of Farms by Parish PARISH SIZE OF FARM Assumption 347 Lafourche 274 St. Charles 546 St. James 371 St. John 309 Terrebonne 308 15,000 field workers in the state. This area having 40.6% of the state acreage has approximately 6,090 field workers. 2,500 direct service industry employees state wide for cane industry. This area is the home of CANICO and Thomson Machinery which are two of the largest cane equipment producers. Source: Interview with American Sugarcane League Official (1979). 128 OTHER CROPS Because of a fluctuating sugar market, other crops have been recent ly introduced into the South Central Region, notably soybeans. Table 2.1 lists the major crops in the South Central District as of 1978. As can be seen from this table, sugarcane is still the predominant crop. Hmiever, soybeans occupy considerable acreage. Present indications are that soybean acreage will continue to slowly increase at the expense of sugarcane in the near future. 129 TABLE 2. 1 Major Crops in the South Central Region 1978 (in acres) PARISH SUGARCANE 1 SOYBEANS OORN2 TRUCK CROPS3 Assumption 34,900 1,500 100 250 Lafourche 32,000 2,300 450 450 St. Charles 1,050 0 50 200 St. John 21)700 6,400 250 150 St. Jams 7,250 2,300 100 150 Terrebonne 13,330 6,000 200 150 Total 110,230 18,500 1,150 1,350 1. Figures indicated are acres harvested for sugar.. Multiply this figure by approximately Wo for total sugarcane acreage. estimate. 2. Corn used mainly for home consumption. 3. Fresh crops are usually consumed at home or used in roadside stands. Sonia exceptions to this include St. Charles Parish where crops are sold to New Orleans because of proximity to the market. Source: Louisiana Ci-ops and Livestock Reporting Service (1979) and Richard Folse, County Agent U.S.A.S.C.S. 130 FAPdvff-AM LOSS Perhaps the biggest future problem that will confront agricultural interests in the South Central District is agricultural land loss to urbanization and industry. Much land has and will continue to be gobbled up by industry and urban spread. This land is usually taken from agri- culture due to the differences in value between land use for agriculture, urban or industrial activities. Table 2.2 illustrates the decrease in crop acreages over a twenty-five year period in our district. It appears that unless agricultural land is viewed as a resource instead of a comnodity, this trend will continue in the innediate future (see Part II, Chapter 4 for a further discussion of conflicts in the uses of land in the South Central District). 131 TABLE 2.2 Total Cropland (1950 - 1975) (in acres minus pasture) PARISH Assumption 56,000 56,000 -0- Lafourche 81,320 72,000 - 9,320 St. Charles 19,000 15,000 - 4POOO St. John 29,000 19,000 -10,000 St. Jams 44,313 39,000 - 5,313 Terrebonne 41,727 38,366 - 3,361 Total 271,360 239,366 -31,994 Source: Louisiana Crops and Livestock Reporting Service (1975) and Richard Folse, County Agent U.S.A.S.C.S. 132 BIELIOGIAPHY Interview with Amrican Sugarcane League Official. New Orleans, 1979. Interview with Richaxd Folse of the Agricultural Stabilization and Conservation Service of the United States Departmnt of Agriculture. March 1980. Rehder, John B. (1978) "Diagnostic Landscape Traits of Sugar Plantations in Southern Louisiana" from Geoscience and Man, Vol. XIX. Louisiana State University, Baton Rouge, Louisiana. 133 CHAFrER 3 - INDUSTRIAL LAND USES By Edwin J. Durabb INTRMUCTION Industrial Land Use, like other land uses in the South Central District is concentrated along the natural levees where the good drainage, soils, and cheap water transportation are available. The following sections will discuss general features of this type of development. Following this, two examples will be selected to illustrate the types of industrial and conn)ercial development prevalent in the South Central Region. E, 49USTRIAL LAM USE There are basically five types of industrial developmnt in the South Central Region. 1. Non oil and gas related industry dependent upon the Mississippi River. 2. Oil refineries and related petrochemical industries dependent on River Transportation. 3. Oil and gas production and support facilities. 4. Nodal development dependent on both transportation and production - support oil and gas facilities. 5. The fishing industry. Table 3.1 lists current values of industria-1 developmnt by parish in the South Central District. Figure 3.1 illustrates the distribution of this investment in the recent past, coapared with the 1978 year. 134 TABLE 3.1 RECENT HISTORY OF INDUSTRIAL. INVESTMENT BY PARISH FOR EAST SO[TTR CENTRAL LOUISIANA PARISH 1972-77 1978 Assumption .................... 9,614,001 $ 11,369,706 Lafourche ..................... 1,191,202 7,435,304 St. Charles ................... 1,454,540,3015 840,657,203 St. James ..................... 163,273,759 282,643,901 St. John the Baptist .......... 363,271,928 46,611,211 Terrebonne .................... 1,548,975 12,800,000 TOTAL $1,993,440,170 $1,201,517,325 Source: Louisiana Dept. of Commerce (1976) page 1. 135 FIGURE 3.1 MANUFACTURING SHIPMENTS AND PLANTS IN EAST SOUTH CENTRAL LOUISIANA, 1977 ST.- Mmm 526.1 11 plants ST. JCEIT ?APTIST ASSUMMON 316.5 = 136. 4 = 8 plants 7 plants ST. CV-RT-ES 987. 6 = 11 plants LAF=HE 235.3 =n 208.7 mm 32 plants 28 plants source: Louisiana Department of carmerce (1979) page 1. 136 THE MISSISSIPPI RIVER PARISHES The South Central Planning and Development Commission parishes of St. James, St. John the Baptist and St. Charles offer excellent sites for the large industrial concerns that have and are continuing to locate there. The following factors have influenced the location and type industries that now cover large areas near the Mississippi River. 1. Availability of cheap transportation for raw materials (Mississippi River). 2. Availability of large tracts of land along the transportation artery (Mississippi River). 3. Cheap, voluminous source of fresh water for industrial processes. 4. Proximity to sources of raw materials (oil and gas). 5. Proximity to a large port (New Orleans). 6. Favorable local governmental attitude in the form of relatively few restrictions and favorable tax status. The predominant industries along the River are oil refineries, related petro-chemical plants and bulk storage facilities for grain and raw materials. An example of this type of industrial development is illustrated in St. John the Baptist Parish. Although each of the three river parishes is somewhat different, this parish can serve as an example of the kinds of industrial facilities that exist along the river. (Figure 3.2 illustrates the types of industries prevalent in all three parishes. 137 FIGURE 3.2 MANUFACTURING LOCATIONS AND EMPLOYMENT LEVELS IN EAST SOUTH CENTRAL LOUISIANA ST. JOHN THE BAPTIST Rubber and Miscellaneous Plastics Products ST.'JAMES Chemicals and Allied Products Sugar Refining Sugar Refining Petroleum Refining Primary Metal Industries ASSUMPTION ST. CHARLES Food Processing Chemicals & Allied Products Chemicals & Allied Products Petroleum Products LAKURCHE Transportation Equipmnt Food Processing TERREBCINTNE :Z= Machinery, except Electrical Transportation Equiprrent Food Processing Manufacturing Employment Legend Machinery, except Electrical 40 10,000-30,000 40 1,000-2,500 5,000-10,000 0 500-1,000 2,500-5,000 .9 Less than -000 Source: Louisiana Department of ConTwrce (1979) page 1. 138 ST. JOHN THE BAPTIST PARISH Genera.1 St. John Parish sits astride the Mississippi River in the north- eastern portion of the South Central District (see Figure 3.2). In 1980, the population of the parish was 23,813 with the 1980 estimate being 35,941. The parish is currently experiencing growth from existing Ld new industry, as well as suburban spillover from the New Orleans area, which is located 25 miles avay. As in other parishes in the South Central Planning & Development Coninission region, this area is predomi- nantly wetland with the two portions of the Mississippi River natural levee, providing the only high developable ground in the area (SCP&DC, 1979). Of the total parish area, of 238,108 areas, only 36,556 areas are not wetland or about 15 percent of the total (Louisiana State Planning Office, 1975). Goverrm)-antal The parish is currently governed under the Police Jury form of government. Due to the splitting of the Parish by the Mississippi River and the lack of a bridge to cross it, parish services must be duplicated on the east and west bank. There are no incorporated municipalities in this parish. 'Ihere are no zoning ordinances or housing codes. There are, however, subdivisions and floodplain regulations. Within a year, a comprehensive Coastal Zone Management Ordinance will be in place to manage and regulate wetlands areas of the parish. 139 Industries Table 3.2 illustrates existing industries in the parish. The major employers are petro-chemical related or plants requiring cheap transpor- tation of raw materials. Table 3.3 illustrates the proposed new industries within the parish as of early 1979. Table 3.4 lists the employment categories in the Labor force in St. John Parish as of 1978. As can be seen, the largest single employer is manufacturing. With the Kaiser Aluminum. plant, and the projected steel mill, there appears to be some trend away from petro-chemical -industries, at least in St. John the Baptist Parish. 140 TABLE 3. 2 Existing Industry Following are the names of most of the manufacturing firms in St. John the Baptist Parish with the size of their work force and their end products. Edgard Caire and Granyard raw sugar 100 Garyville Marathon Oil Company energy products 195 NALOO Chemicals chemicals and chemical preparation so Laplace Castro, Inc. wood pallets and sheds 8 F & M Concrete Compan, Inc. ready-mix concrete 10 Riverlands Publishing Company printing 15 E. I. Dupont de Nemours chemicals 525 Reserve Cargill, Inc. grain elevators 60 The Ceco Company Continental Elevator Company grain elevators 60 Datalog, Inc. oil field service 35 The Dorsey Corporation Filter Media, Inc. perlite products 20 Jones Chemicals, Inc. chemicals 20 St. John Shipping Company Shelter Industries construction materials 40 Nit. Airy Mt. Airy Refining Coapany energy products 50 St. John - St. James Parish Line Kaiser Aluminum & Chemical Company primary aluminum 1,030 Source: South Central Planning & Develop-a-ent GonTnission, 1979. 141 TABLE 3.3 St. John The Baptist Parish Proposed Industry Garyville Liquechemica of America chemical products .100 LaPlace Bayou Steel steel bi-Ilets 625 Wallace Shell Cherrdcal chemical products 100 Reserve Browning-Farris Industries truck repair facility ? Continental Plastics manufacturing warehouse Mississippi Valley Equipnie-nt heavy equipmnt yard Source: South Central Planning & Development ConTnission, 1979. 142 TABLE 3.4 St. John `Ihe Baptist Parish Employmnt By Industry, 1978 Occupation Nurrber of 1hployees Agriculture, Forestry, Fi�hing 312 Mining 94 Construction 660 Manufacturing 2,293 Transportation, Communication, and Utilities 513 Wholesale and Retail Trade itill Finance, Insurance and Real Estate 196 Services 992 Goverment 150 TOTAL 6, 321 Source: South Central Planning & Developmnt Comission (1979). 143 OIL AND GAS EXPLORATION AND SUPPORT FACILITIES: UM CDASTAL PARISBES The other main type of industrial development prevalent in the South Central Region is that of direct and indirect exploration and support facilities associated with the locating, drilling and storage of oil and gas. This includes such activities as ship building (mainly barges and crewboats) catering, welding, machine shops, oil rig fabri- cation, etc. The predominant factors that have in the past, and still do provide the stimulus for industrial location are: 1. Source of cheap transportation (water). 2. Location neax the source of resources (oil, gas, sulphur, fish, shrimp, etc.). 3. Availability of land to build industries. 4. Lack (especially in the past) of goverrmiental controls that would restrict development. Of. the total land/water acreage of 1,338,387 acres, 231,192 acres or about 17 percent of the total area is natural levee or drained wet- land area (Louisiana State Planning Office: 1975). 'Ihe estimated 1980 population for Lafourche Parish is 76,537. Development here, as elsewhere in the district, is st#p, development, mainly along Bayou Lafourche. There are three incorporated comamities in the parish. These are `Ihibodaux, Lockport and Golden Meadow. Of these, only Thibodaux is of substantial size (14,925 with an estimated area population of 20,000) (Munphrey et al 1976: 2-3 and Author). 144 Governmental 'Ihe parish is currently governed by the Police Jury system of gov- ernn-ent. After mid 1980, however, Lafourche will switch to a more sophisticated President-4Council system of government. Each unincorpor- ated comnunity within the parish is under a variety of the Mayor-Council f orm of government. Land use controls in the parish consist of Subdivision and Mobile Home Regulations, Flood Plain Regulations and, within a year, canprehen- sive Coastal Zone Management regulations. 'Ihe cities of 'Ihibodaux and Golden NLeadow currently also have Zoning Ordinances in force. Industrial Development The parish can be broken down into these areas: 1. The northern agricultural area from the northern parish line to Raceland 2. `Ihe central transition zone from Raceland to Larose, north of the Intracoastal Waterway 3. The southern zone from Larose, south of the Intracoastal Waterway to the Gulf of Mexico In the northern zone, agriculture and farm processing are the pre- dominant industries. In the transition zone, both agriculture and related oil and gas industries exist. In the southern zone, industries related to oil and gas, and the fishing industry predominate. Table 3.5 illustrates the main industries in Lafourche Parish. Note the concentration of fishing and oil and gas related industries in the southern portion of the parish. 145 Table 3. 5 MANUFAC=RS IN LAFOURCHE PARISH (1972) sic Number of Code Location Product Description Employees 2036 Leeville fresh and frozen shrimp 20-49 2036 Golden Meadow fresh and frozen shrimp 90-197 2042 Golden Meadow animal foods 40-98 2051 Golden Meadow bread and pastries 20-49 2499 Golden Meadow travel boats 1-7 3599 Golden -Meadow mchine shop, jobbing 20-49 and repair 3732 Golden Meadow boat repair 8-19 3711 Cut Off amphibious tractors 20-49 3731 Larose steel tugs, barges,push 40-98 boats, shrimp boat building and repair 2061 Lockport sugar and molasses 50-99 2086 Lockport soft drinks 8-19 2621 Lockport plup and paper 250-499 3731 Lockport tugs, push boats, barges, 200-498 offshore support vessels, marine repair 2061, 2 Matthews & raw sugar, refined sugar 200-498 Raceland. black strap mlasses 2329 Matthews & sports clothing 50-99 Raceland 2013 Thibodaux slaughtering plant, 50-99 sausages 2026 Thibodaux milk products 20-49 2061 Thibodaux raw sugar, molasses 200-447 2071 Thibodaux candy 50-99 2086 Thibodaux soft drinks 50-99 2751 Thibodaux ccmercial printing 20-49 3443 Thibodaux pressure vessels, storage 100-249 tank 3522 Thibodaux tractors, side hoe 200-498 ditches 3599 Thibodaux mchine shop service for 50-99 oil and sugar industries 3711 Thibodaux draglines, personnel 50-99 carriers, drill rigs 3732 Thibodaux small boats 20-49 Source: Gulf South Research Institute, 1974: 32. 146 Tables 3.6, 3.7, and 3.8 illustrate the historical development of the oil, gas and sulphur industry in Lafourche Parish (MuTrphrey et al 1976: p. 913). Table 3.9 illustrates employment in related oil and gas activities in Lafourche Parish in the yeaxs 1964-1973. Table 3.10 illustrates the trends in oil and gas production toward offshore Louisiana in recent years, as onshore resources have dwindled. Fishing industry statistics for employment are listed in Table 3.11. Seafood landings are listed in Table 3.12 (see Chapter 7, Paxt I and Chapter 4, Part II of this report for more information on the fishing industry). The preceding two examples are illustrative of the various kinds of industrial development in the SCP&DC region. Although difficult to predict, future trends appear to be: 1. Tightening of governmental restrictions at the local, state, and federal level regarding: a) air pollution b) water pollution c) solid waste disposal d) land use interaction 2. Slow decline in oil and gas related exploration activities in the lower parishes. 1It must be noted here that the author has noticed that many small asso- ciated industries in lower La-fourche Parish have not reported, or axe not listed in the available surveys, thus resulting in an undercount of employees and industries. 147 TABLE 3.6 LANDMARKS OF RESOURCE DEVELOPMENT IN LAFOURCHE PARISH OIL 1902 First oil field in Louisiana began production at Jennings salt dcme in Acadia Parishl. 1922 First permit for exploratory drilling in Lafourche Parish issued by Minerals Division, Louisiana Department of Conservation2. 1928 Leeville Dcme discovered by seismograph3. 1931 First commercial production of oil in Lafourche Parish at Leeville Dome began in February when Texas Company completed their first producing well. It produced 157, 675 barrels for the year3. 1932 A second well (by Pop Oil Company) began producing 90 barrels daily, for a total production by the Leeville field of 267, 962 barrels for the year4. 1933 Eight producing wells were completed at Leeville for a total pro- duction of 361,000 barrels4. 1934 Fifty-two (52) producing wells were coVeted at Leeville Field. Total production was 4,329,572 barrels 1935 Nine (9) new prodicing wells were completed at Le-eville, increasing yearly production to 4,820,093 barrels4. 5 1936 Oil production declined somewhat to 4,596,027 barrels 1937 Producing wells were established at Harang Field and Lake Lond Field. Total production: Harang 977,862 barrels Lake Long 83,231 barrels Leeville 2,651,187 barrels TOTAL 3,712,280 barrels 1940 Lafourche Parish produced a total of 7,926,467 barrels (including condensate)6. 1941 Lafourche: Parish produced 8,958,960 barrels6. 148 TABLE 3.6 CONTINUED 1947 First offshore well in Louisiana started and completed by Kerr-McGee Oil Ccmpany in Ship Shoal Area off Terrebonne Parish7. 1949 First oofshore well off Lafourche Parish, discovered by the Califor- nia Ccimpany in Bay Marchand Field, was completed on March 3rd7. 1970 Production of oil in Lafourche and offshore Lafourche was 117,674,244 barrels8. 1971* Production in Lafourche and smaller offshore area was 89,676,024 barrelO. 1972* Production in Lafourche and still smaller offshroe area was 58,548,420 barrels8. 8 1973* Production decreased in same area as 1972 to 53,022,060 barrels *Offshore area decreased because of increasing Federal jurisdiction off- shore. These statistics were collected by the Louisiana Department of Conservaiton in its jurisdictional area. Source: Muaphrey et al (1976) pages 10-11. 149 TABLE 3.7 IANDMARKS OF RESOURCE DEVELOPMENT ]IN LAFOURCHE PARISH NATURAL GAS 1909 Gas was discovered at the Monroe Gas Field in Ouachita, Morehouse, and Union Parishes, but the first ccmTbercial gas was not produced until 19163. 1916 The 1914-1916 Report of the Depaxtment of Conservation states that, "The total production of gas for the year 1915, as nearly as can be estimated, is 27,261,260,000 cubic feet . . . Formerely, no accurate records have been kept on the gas production and it is impossible to obtain positive information, except frcm the producers who have kept records of their production." In light of this, the earliest record of gas production in Louisiana that could be found was in 1912 from the Bull Bayou Field in DeSoto Parish9. 1938 First natural gas to be produced in Lafourche Parish was at LeevillelO. 1939 Gas was alsp produced frcm fields at Raceland and Valentine (Harang) for a total production as follows: Leeville 131,290 M.C.F. Raceland 351,022 M.C.F. Valentine 92,794 M.C.F. TOTAL 575,105 M.C.F. 1940- Production fluctuated, averaging approximately 16,600,000 M.C.F. 1950 for the periodll. 1948 First offshore gas discovered in the Grand Isle area. 1951- Production increased steadilyl2. 1968 1969 Production of natural gas reached its peaks of 318,800,130 M.C.F. for the year8. 1970- Production dropped to 275,434,479 M.C.F. as offshore area for which 1973 data was provided gradually decreased*. Source: Munphrey et al (1976) pages 11-12. TABLE 3.8 IANDMARKS OF RESOURCE DEVELOPM= IN 1AFOURCHE PARISH SUPHUR 14 1927 Sulphur discovered at Chacahoula Salt Dcme by Gulf Refining Ccmpany 1955 First ccmercial sulphur production in Lafourche began on March 10 by the Freeport Sulpi= Company. 1960 The world's first offshore sulphur mine began production in the Grand Isle area. 1962 Ccmercial production at Chacahoula ended in Septenber. 1967 Sulphur production began again in Chacahoula. 1968 Production began at Bully Camp Dome by Texas Gulf Sulphur Company. 1970 Production stopped at Chacahoula, but continues at Bully Camp. 1973 Natural gas shortage and oversupply of sulphur results in reduced production at Bully Camp. Source: Mzrphrey et al (1976) pages 11-12. 151 TABLE 3.9 EMPLOYMENT. IN OIL AND GAS RELATED PRIMARY AND SECONDARY-INDUSTRIES IN LAFOURCHE PARISH sic Code Industry 1953 1956 1959 1964 1965 1966 1968 1969 1970 1971 1972 1973 PRIMARY INDUSTRIES Mining (total) Errployees 1602 1206 784 2149 1916 2207 1630 1146 1183 1070 1302 1245 Payroll ($1000) 1664 1672 '1277 3208 3128 3505 3384 2314 2600 2709 2455 3169 Establishments 36 34 18 51 41 50 44 37 38 35 38 38 13 Crude Petroleum and Natural Gas 2 Employees 1206 D 2149 1916 2207 D D 1183 1070 1302 1245 Payroll ($1000) 1672 D 3208 3128 3505 D D 2600 2709 2455 3169 Establishments 34 16 51 41 50 43 36 38 35 38 38 131 Crude Petroleum and Natural Gas Employees 467 447 D D D D D D D 501 483 Payroll ($1000) 713 806 D D D D D D D 1417 1456 Establishments 10 10 16 12 20 10 8 11 10 9 9 132 Natural Gas Liquid Employees D D D D D -- -- -- -- Payroll ($1000) D D D D D Establishments 2 1 1 2 2 TABLE 3.9 CONTINUED sic Code Industry 1953 1956 1959 1964 1965 1966 1968 1969 1970 1971 1972 1973 138 Oil and Gas Field Services Errployees 739 D 1545 1354 1635 1116 621 678 562 801 755 Payroll ($1000) 959 'D 1990 2035 2311 2211 1068 1346 1315 1538 1702 Establishments 24 6 33 28 29 31 26 26 24 29 28 1381 Dtilling Oil and Gas Wells En-ployees D 765 D 871 750 312 307 228 321 299 Payroll ($1000) D 1346 D 1354 1618 559 566 522 528 665 Establishments 5 16 12 14 11 9 7 7 8 7 1382 Oil and Gas Exploration Services E@Tployees D Payroll ($1000) D Establishmehts 2 1389 Oil and Gas Field Services, n.e.c. (not elsewhere covered) Effployees D 647 D 290 264 297 307 408 378 Payroll 0@1000) D 861 D 522 461 708 775 954 954 Establishments 15 14 13 15 13 14 14 18 17 44 Water Transportation ErTployees 672 655 933 1100 1455 1557 1585 1869 1871 2076 2401 Payroll ($1000) 507 587 971 1175 1707 2155 2271 2759 2893 3234 3746 Establishments 98 123 130 132 152 146 141 157 166- 181 192 TABLE 3.9 CONTINUED sic Code Industry 1953 1956 1959 1964 1965 1966 1968 1969 1970 1971 1972 1973 445 Local Water Transportation Employees 524 844 992 1335 1395 1412 1707 1764 1916 2137 Payroll ($1000) 484 871 1049 1556 1935 2060 2528 2703 3001 3393 Establishments -117 112 115 113 130 126 140 151 163 165 446 Water Transportation Services Employees 74 D D D D D D 148 202 Payroll ($1000) 84 D D D D D D 211 272 Establishments 14 14 17 14 14 16 14 15 18 4469 Water Transportation Services, n.e.c. (not elsewhere covered) Employees 74 D D D D D 148 202 Payroll ($1000) 84 D D D D D 211 272 Establishments 14 14 14 14 16 14 15 18 SECONDARY INDUSTRIES 162 Heavy Construction, n.e.c. (not elsewhere covered) Employees D D 221 226 463 108 199 171 212 ill Payroll ($1000) D D 248 290 688 158 306 320 441 211 Establishments 9 14 13 12 18 11 10 12 10 9 TABLE 3.9 CONTINUED sic Code Industry 1953 1956 1959 1964 1965 1966 1968 1969 1970 1971 1972 1973 35 Machinery, Except Electrical (Manufacturing) Employees 137 154 D D D 259 231 209 213 238 Payroll ($1000) 135 150 D D D 399 366 359 376 444 Establishments 3 5 2 4 4 5 6 '6 7 8 37 Transportation Equipment Employees 254 311 268 258 233 220 221 241 328 Payroll ($1000) 273 338 403 402 399 367 428 518 617 Establishments 14 12 10 11 12 9 10 10 11 373 Ships and Boats Employees D D D D D D D@ D 160 Payroll ($1000) D D D D D D D D 506 Establishments 13 11 9 10 11 8 9 9 9 3731 Ship Building and Repairing Employees 108 169 D 142 D D Payroll ($1000) 136 298 D 306 D D Establishments 4 5 3 3 3 4 TABLE 3.9 coNTiNuED DIC @ode Industry 1953 1956 1959 1964 1965 1966 1968 1969 1970 1971 1972 1973 3732 Boat Building and Repairing Employees 156 193 191 D Payroll ($1000) 177 218 262 D Establishments 10 8 7 6 308 Machinery, Equirment and Supplies Mhe)lesale Trade) Employees 133 121 Payroll ($1000) 203 244 Establishments 11 11 OTE: 'These date are taken from County Business Patterns for the years indicated. The en-ployment data from this publication does not include government employees, self-employed persons, farm workers, and domestic service workers. Also, rail- road employment subject to the Railroad Retirement Act and employment on oceanborne vessels are not included (Bureau of the Census, 1973: 1). While these exclusions are not considered to seriously affect the figures for the industries, the exclusion of self-employed persons my cause these figures to be slight understatement of the actual exrployment. Also, the exclusion of government employees has resulted in a failure to note the effect of OCS development on relevant government agencies, such as the U.S. Geological Survey and the U.S. Army Corps of Engineers. 2Figures withheld to avoid disclosure of operations of individual units. ;ource: Mmphrey et al (1976) p. 15-19 TABLE 3.10 PERCERr OF OFFSHORE OIL AND GAS PRODUCTION IN THE HOUMA DIsmicrl 1958 1959 1964 1965 1966 1967 1968 1969 1970 Crude Oil and (bndensate 21.0% 18.67o 37.6% 39.1% 42.9% 44.1% 48.0% 52.3% 54.4c/'O' Casinghead and Natural Gas 10.0% 13.1% 12.67o 14.1% 17.3% 18.87o 21.6% 24.67o 30.57o This table indicates the increasing importance of offshore production. The percentages were computed from the' production statistics of the Louisiana Department of Conservation. The 1958 and 1959 figures refer to offshore production in the South Louisiana area, while the 1964-1970 figures are for the offshore production in the Houma district, which includes the parishes of Terrebonne, Lafourche, Assumption, St. Charles, St. John the Baptist, St. James, and parts of St. Martin, Iberia, Iberville, and Ascension parishes. It also includes the offshore areas of Ship Shoal, South Pelto, South Timbalier, Bay Marchand, and Grand Isle. After 1970, the federal government assumed jurisdiction for a portion of the Houma District. The Department of Conservation figures for offshore production after 1970 include only a portion of the total offshore production and it was decided not to include them in this table. Source: Murphey et al (1970) page 75. TABLE 3.11 BTLDYMENr IN SEMMD INDUSTRIES IN LAFOURCME PARISH FOR 1975-1976 BY QUARTER* SIC Number Description 1975-1 1975-2 1975-3 1975-4 1976-1 0910 CaTmercial fisheries 86 109 120 118 79 0912 Finfish 5 5 10 7 10 0913 Shellfish 90 129 154 139 126 0989 Fish hatcheries, farm, and 8 13 15 18 10 preserves Cn Go TOFAL 189 256 299 282 225 *Because of disclosure problem relating to.single-fim industries, Table 3.11 should not be further repro- duced without the permission of its source. Source: Murphrey et al (1976) page 166. TABLE 3.12 OOMMERCIAL.SEAFOOD LANDINGS FOR GOLDEN MEADOW-LEEVILLE PORT Size Value Year (1000 lbs.) ($) 1972 37,900 9,100,000 1973 32,565 8,626,000 1974 26,819 8,000,000 1975 23,395 11,260,000 Source: Aka*phrey et al (1976) page 167. 159 3. Continuing industrial expansion in the "River Parishes". 4. Relative stability in the fishing industry. 5. Increasing land use conflicts as industry competes for space with other development (especially in the "River Parishes"). Conflicts in land use between Industry, Population and Agriculture are discussed in the next chapter. .160 BIBLIOGRAPHY Louisiana Department of Comwrce, Office of Camierce and Industry, (1979) "Louisiana Business, Volume 2 - Number 5". Baton Rouge, Louisiana, Louisiana Departmnt of Com-nerce and Industry. Louisiana State Planning Office (1978) Land Use and Data Analysis. Baton Rouge, Louisiana, State Planning Office. Mumphrey, et al (1976) The In-pacts-of Outer Continental Shelf Development on LaYo-tEc-he Paxish. New Orleans, Urban Studies Institute, Univer- sity of New Orleans. South Central Planning and Development Commission (1979) St. John the Baptist Parish: The Center of Louisiana's Industrial Growth. Thibodaux, Louisiana, South Central Planning and Development Commission. South Central Planning and Development Commission (1980) unpublished High Altitude Infrared Photographs taken by the National Aeronautics and Space Administration, December, 1978. 161 CHAFM 4 - CaNULICTS IN LAND USE By Edwin J. Durabb INTRODUCTION In the South Central District there are many conflicts between the land uses of man and the natural system. There are also conflicts be- tween the resource uses to which the land has been put in our district. `Ihis is not an unusual situation in that every area of the country has conflicts in utilizing the land and its resources without destroying the integrity of the natural order. What is unique here is the dynamic and fragile ecological and geomorphic system that exists in the landscape. The very fact that we inhabit and modify this area has profoundly changed the evolution of this landscape. Conversely, the local environment has largely shaped what we do and how we do it in response to the natural constraints of the land. This chapter attempts to identify conflicts, explain them and investigate what is currently being done to resolve competing land uses. The main areas of conflicting uses involve the following: A. Uses of the Land Versus The Environment 1. Utilizing the Natural Levees a. flood protection costs to man b. flood protection costs to the environment 2. Utilizing the Wetlands Area a. reclamation b. harvesting natural renewable resources C. recreation d. transportation. 162 B. Conflicts Between the Uses of Man 1. The Natural Levee a. agriculture versus urban expansion b. agriculture versus industrial and comwrcial development C. residential versus industrial development d. waste disposal, pollution. 2. Wetlands a. oil and gas exploration versus the fishing industry b. reclamation C. mitigation These conflicts will be examined and discussed in the following sections of this chapter. 'Ihe conflict descriptions related here are primarily verbal non-quantitative discussions of the problems in land utilization between man and nature and various uses of man. In the next phase of this report, statistical land use camarisons and change assessment will be made to document the problems identified in this chapter. USES OF - THE LAND VERSUS TEE ENVIRCNMENT Utilizing the Natural Levee Flood Protection Costs To Man As mentioned in Part I of this report eighty-one percent of our district is classified as wetlands or water. The other nineteen percent is either reclaimed or "natural levee" lands that are normally dry. In either case, extreme methods must be taken to keep our land dry and protect the residents who live here. 163 History As soon as settlers began to carve out the local wi-Iderness, it became apparent that coexistence with the natural order would be diffi- cult at best. The saw river that built the fertile land of the area flooded almost yearly, depositing lifegiving silt, but in the process destroying lives and property. Efforts to modify the natural system for flood protection began quite early in the recorded history of the area: French settlers were the first recorded builders of flood control works in the Lower Mississippi Valley. It was in 1717 that the founder of New Orleans, Sieur Jean de Bienville, had his engineer, Sieur de la Tour, construct a series of protective levees to hold back the floodwater from the town. By 1735, the levee lines on both sides of the river extended frcm about 30 miles above New Orleans to about 12 miles below the city. Floods alternated with progress on the system, but, by 1812, levees extended upriver to Baton Rouge on the east bank and about 40 miles beyond Baton Rouge on the west bank. By 1849, the west bank levees reached almst as far up as the Arkansas River in an almost continuous line, and isolated levees had been built along the east bank to protect land in the Yazoo Basin of Mississippi. U. S. Army Corps of Engineers, (1970). These levees helped protect the people who lived on the delta, but could not contain severe floods along the river. Levee building continued off and on into the twentieth century, but this was still not enough to protect the residents from flooding. The disastrous river flood of 1927 covered 26,000 square miles of the Mississippi Valley and spurred Congress to pass the Flood Control Act of 1928 mandating Federal involve- ment. From that date to the present, billions of federal dollars have been spent to protect the Mississippi Valley and Delta area from flooding. 164 Protective measures include levees along the Mississippi that top twenty- five feet in height and flood control structures to divert Mississippi River water during periods of severe flooding. In Louisiana, Flood control structures at the "Old River", "Morganza!' and "Bonnet Carre" divert millions of cubic feet of river water during floods. Figure 4.1 illustrates the intricate system of revetments, dikes, spillways, levees and artificial cutoffs that have been executed to prevent major flooding here as well as in the Upper Mississippi Valley. Local flooding from rainfall and the local share of levee construc- tion must be borne by the local taxpayer. In addition to the river, lower portions of the natural levees are vulnerable to flooding from hurricane storm surges. Thus, "back levees" must be built to protect the rear areas from this danger, and pLunps must be utilized to secure water trapped inside the system. Flood Protection Costs to the Environment Man has largely protected the natural levees from flooding by the Mississippi River overflow and storms from the Gulf of Mexico. This protection, however, has had disastrous impact on the ecosystem. Preven- tion of flooding by the Mississippi system has had the following nega- tive effects: 1. Loss of freshwater to the estuary system a. lack of flushing of the system b. reduced capacity to assimulate pollutants C. increased salinities in the lower basins d. loss of natural source for the estuary 165 FIGURE 4.1 Ct Q. MISSOURI R 100,000- ST. LOUIS 4 IV Ft CAIRO 0 0 NEW MADRID FLOODWAK",' z --, 6 0 PADUCAH NEW MADRID C; MEMPHIS NOTE HELENA ARKANSAS R Decredse in stream flow i3 400,000 - 540,000 occdsianed by chdnnel dnd bdckwcitcr itora5re. ARKANSAS CITY OIL Qz Cm A GREENVILLE Ivep p YAZ 0 0 -A Z5, VICKSBURG Q cAL C> LO 5, CJ 2NATCHEZ WEST A T CHA FA L AJvA FLOODWAK 620,000 CQ. C> RED RIVER LANDING ICp 600,000 BATON BONNET CARRE ROUGE CD Qz MORGANZA SPIL. L WAY Cr CD FLOODWAY 50.00 - WAX LAKE OUTLET LAKE I N P0,VrCHARrR,4ljV -4 IM NEW CD MORGAN ORLEANS CITY 0 PROJECT DESIGN FLOOD vr WA r 0 0 p (58 A - EN) CuBiC FEET PER SECONO SEPT. 1958 t Source: U. S. Army Gorps of Engineers, (1973) p. 11. 166 2. Loss of Silt and Clay Deposition a. cessation of land building b. loss of needed nutrients in the estuary C. contributing factor to rate of land loss in the coastal zone In Chapters 5 and 7 of Part I of this report, the vegetation and ecosystem function of the estuary system was discussed. Freshwater and silt are needed components to maintain the system. As the river shifts its course, there is always land loss on the old delta and land gain in the new deposition area. Without new silt, however, there is little or no land gain (since the River currently has been channeled to the point of dumping its silt load off of the continental shelf and not across its deltaic plain. The only freshwater input into the system is gotten from rainfall, natural levee runoff, urban runoff and canal leakage (mainly navigation canals on the Mississippi River). This water amount is miniscule when compared to what cam before levee construction. This freshwater is also polluted with urban and agricultural wastes causing eutrophication (choking of a body of water by the natural or artificial introduction of nutrients) of the lakes near urban or agricultural areas. Craig and Day (1973), have documented the detrimntal effect this has had on the Barataria Basin, an area responsible for forty-five percent of the State's total commercial fish harvest. Utilizing the Wetlands Area This section will deal with the effects of man's use of the vast areas of wetlands within the South Central District on the natural 167 system on our region. Habitation of wetland areas and resource use conflicts will be the tv)o topics of discussion since they constitute the largest irrpacts on the natural system in our area. Reclamation It is impossible to build waters, cities or accomplish any other intensive activity in a wetland area in its natural state. Therefore, very early in the history of settlement of the region, efforts were made to "reclajlV' land areas from their natural wet condition, drain them and utilize the axea for an intensive activity usually farming or urban type development. Such land once drained was called "first land". It was protected from frequent flooding and therefore suitable to use for man's activities. When land is reclaimed, several negative effects occur on wetlands. These are all :@elated to the loss of land to the estuary. These are: 1. irreversible loss of land to the estuary 2. loss of habitat for birds, fish, etc. 3. Loss of nursery area for birds and fish 4. loss of "detritus" providing area to the estuary 5. eventual drop in estuarine productivity in the absence of any compensating factors. The function of the wetlands ecosystem has been discussed in Part I of this report. Draining of these wetlands cause subsidence because of the withdrawal of water from the soil and oxidation of peat deposits (accumulations of partially decomposed vegetable matter). Thus, even if artificial levees were eventually torn down and the pumps turned off, 168 the area would revert to open water, not wetland, thus causing the effects listed above on the ecosysten. Reclamation Projects in the South Central. District Most of the reclamation in the South Central District has been for agricultural purposes (see Table 4.1). Very little wetland has been a1tered for urban use in our district. This contrasts sharply with the adjacent New Orleans Area, where roughly 102 square miles of wetland in Orleans and Jefferson parishes have been converted to mainly urban areas (Mumphrey, et al, 1975). Harvesting Natural. Resources: Channelization Much damage has been done to the wetlands of the South Central District for the sake of harvesting our natural resources. This includes the mining of sulphur, salt, oil and natural.gas, gen eral navigation, fishing, and drainage. Table 4.2'lists the amount of land that has been taken up in our wetlands of Louisiana by channelization. Canals cause several problems to the Wetlands through which they axe dug. Some of the problem are: 1. interfering with sheetwater flow through the marsh 2. a1lowing rapid salinity change with resultant death of vegetation and erosion (widening of the channel) of the marsh 3. allowing destruction of the marsh by wave action 4. decreased productivity by the presence of straight versus sinuous channels that accelerate removal of freshwater and also confine water movement (and detritus) 169 TAELE 4. 1 "Major Reclamation Projects in the South Central District to 1961" 1. St. Charles Municipal Drainage District No. 1, also known as Sunset Drainage District; about 10,000 acres. (Several projects started in this area in early 19001s; only one remains.) Flood overflowed district in 1912. Drainage local and inadequate. Only 25 to 30 percent of land in agriculture, used mainly for pasture and forage crops. Land now owned by corporation, and oil deposits being developed. Once settled by Corn Belt famiers; all of them now displaced. (See Allemands Quadrangle, U. S. Geological Survey.) 2. St. Charles Drainage District No. 1 (1910); 2,800 acres. Drowned fields now used by duck hunting club. 3. Lafourche Drainage District No. 6 (1910); 1,800 acres. Drowned fields not used by duck hunting club. (See Allemands Quadrangle, U. S. Geological Survey.) 4. Lafourche Drainage District No. 12; 8,265 acres, conposed of sub- districts listed below. Part of project is above local water level and has loamy soil favorable for corn. Lower areas never suitable for small farmrs. Corn Belt farmrs failed. No intensive use of land developed and corn remains principal crop, although some grass seeds have been produced. (See Houna Quadrangle, U. S. Geological Survey.) 5. Subdistricts 1, 2, 3 of Lafourche Drainage District No. 12 (1907); 835, 940, and 2,250 acres respectively. Small fanns at first sold to Corn Belt faxmrs who failed. &nall faxms in area took over but have not made success of fanning. No high-value crops produced, and high drainage taxes mt with difficulty. Now extensive repairs and renovations necessary and no money for this work is in sight. 6. Subdistrict 4 of Lafourche Drainage District No. 12 (1913); 41,240 acres. Became the property of engineering company which developed Nos. 7 and 8 above. Operated as private holding along plantation lines, specializing in beef cattle. Serves a@ kind of luxury farm on which expenses have been heavy, profits fran agriculture rare ano subsidies have been conmn. Oil now helps sustain operations. 7. Smithport Plantation (1907); 947 acres. Original drainage reservoir capacity inadequate and so was enlarged. For a time land was well drained, although tropical sto= did serious damage and hindered purrping operations. Serious condition of soil acidity developed after several years of fanning. Project now abandoned. (See Houma Quadrangle, U. S. Geological Survey.) 170 8. Lafourche Drainage District No. 13, Subdistrict No. 1 (1914); 2,000 acres. Development cost underestimated and project abandoned after spending funds frord $60,000 bond issue. (See Houma Quadrangle, U. S. Geological Survey.) 9. Delta Farms (4 units) (1910-1913); acres range from 600 to 3,000 acres. nu-\--e smallest units abandoned, one of them now serving duck hunting club. Large unit of 3,000 acres survived with heavy losses and subsidies. Changed ownership several times and is now owned by corporation. Owners interested in oil prospects. Operated as stock farm; corn main cultivated crop. Levees and drains in deteriorated state. One of two major pump projects that survives. 10. Clovelly Farms, Subdistrict No. 1 of Lafourche Drainage District No. 20 (1916); 2,500 acres. Private reclamation developed by Northern man as demonstration project. At first operated under tenant system, which failed; now operated under central management. Problem similar to those of other projects but efforts to succeed more persistent. Newly drained land was difficult to cultivate. Bogshoes on horses and special plowing equipment were used. Seven to eight years elapsed before soil was sufficiently dry to be plowed readily and by that time soil was so acid that crop production seemed impossible. Sulphates left by sea water turned acid as they decomposed. Application of lime offered only partial relief. 12 to 16 tops of calcareous sand applied per acre and mixed with peat soil to improve its structure. Now potatoes, corn, cane, cotton and several vegetable crops are grown. Pasture and livestock programs are small. It is still difficult to keep the project out of the red and much investment must be charged to experimentation. 11. Avoca Drainage District (1912); 13,200 acres. Project seriously damaged by flood of 1927. Over one-half million dollars spent on project. Fields aa-e now flooded and serve duck hunting club. 12. Upper Terrebonne Drainage District (1912); 4,240 acres. Storms and seepage proved major problem as dis disagreements between settlers and land development company. Project abandoned. Source: Gagliano (1973) p. 14-17. 171 5. destruction of Barrier Islands with resultant increased destruction of marsh 6. introduction of urban and agricultural pollutants to retard life processes and cause deterioration in the vegetation. One of the prim requiremnts for our estuarine basin is slow water "sheetflow" that allows gradual mixing of salt and fresh water, good nutrient exchange between wetlands and water, and pern-kment water cover to protect wetland soils from oxidation and subsidence. Canals short circuit all of these functions by their straightness, depth, and spoil banks. Canals through barrier islands interrupt sand transport flows, causing erosion of the islands that protect the fragile wetlands behind them. Death of vegetation near canals makes the loose organic soil- highly vulnerable to erosion. The result of this process is accelerated land loss in the wetlands areas. Gagliano and Van Beek (1970) have calculated land loss in coastal Louisiana to be about 16.5 square miles per year and accelerating. Gagliano (1973) has also estimated that roughly 45 percent of this land loss was due to man-made features. Table 4.2 sum-arized land loss from natural and man-made sources. Figure 4.2 graphically illustrates areas of land loss in coastal. Louisiana. From this and other studies, it is evident that land loss is high and increasing in rate over tim. The man-produced features that cause land loss will eventually hasten the deterioration of ecosystenis at a rmch faster rate than the natural system operating alone and unincu-nbered (i.e. natural deterioration of abandoned delta's). Although the fishing industry and other irdneral activities (salt and sulphur) have contributed to man-made land loss, 172 TABLE 4. 2 Surface Area of Natural and Manmade Water Bodies, 1931-1942, 1948-1967, and 1970 Date-or Interval Total Natural Manmade Water Area Water Bodies Wqer Bodies Canals Po Mi2 Mi2 @ti Aji2 1948-1967 maps 6608.17 6381.12 227.05 189.13 37.93 1931-1942 maps 6231.82 6175.25 56.57 40.28 16.29 376.35 205.87 170.48 148.85 21.64 1970 (Projected) 6797.98 6505.31 292.67 245.87 46.80 Elapsed period between the average date of the tm series of maps from which the measurements were taken equals 22. 8 years. Using the f igures above and this elapsed time the following rates can be calculated: Total rate of land loss 16. 51 rrd2/year "Natural" land loss 9.03 mi2/year Manmade land loss 7.48 mi2/year Land loss attributed to canals 6.53 mi2/year Land loss attributed to ponds .95 mi2/year Source: Gagliano (1973) p. 9. Pi gure 4. 2 01 Q LAND LOSS ACRES PER YEAR 0-50 Q- T 50-100 IBM 100-200 VlZO 200-300 [7@77 300-oboVe 0 10 20 :110 40 50 MILES F Source: Gagliano and Van Beck (1970) the oil and gas industry and general navigation canals have been the major cause of this deterioration. Recreation This activity has been of relatively minor impact on wetlands areas. This chief negative effect is that of pollution of waters near large nunbers of camps from sewerage and solid wastes. Transportation Much damage has been done to wetlands by transportation systems, especially highways, both directly and indirectly. Table 4.3 lists highways in the South Central District that cross wetlands areas. The construction of these highways through wetlands areas directly destroy wetlands and blocks drainage. Indirect effects are the stimula- tion of reclamation development. Access is an important factor in any reclamation project. The roadway provides such access. Railroads have also spurred reclamation efforts but to a far less extensive degree. CaNFLICTS BEIVEEN THE USES OF MAN The Natural Levee Agriculture Versus Urban Expansion Since the population of our region is growing, and only eighteen percent of our land area is not wetland or water; and since conuiercial and industrial land uses have expanded; and since the entire land area of the natural force has been utilized; and since the natura.1 levees are not getting any larger, it is logical to assume that some of the uses of 175 TABLE 4. 3 Highways CrossingWetlands Areas In The South Central District U. S. Interstate 10 U. S. Interstate 55 U. S. Highway 90 LA Highway 1 LA Highway 20 LA Highway 307 IA Highway 309 LA Highway 398 LA Highway 24 LA Highway 70 I-A Highway 315 LA Highway 57 LA Highway 56 ILA Highway 55 LA Highway 665 LA Highway 401 LA Highway 402 Source: Louisiana Departmnt of Public Works (1974). 176 man will suffer in relation to others given these parameters. Agricul- ture has been that land use. The soaring value of land in the South Central District and the econcmic woes of sugarcane farming (see Part II, Chapter 2) have made it quite attractive to sell good farmland for other uses. Agriculture Versus Urban Expansion Although expanding cities and non-urban residential expansion is a problem everywhere, the previous, limited levee soils with their good drainage and high elevation are prime candidates for residential devel- opment. Tremendous expansion has taken place in the unincorporated areas of LaPlace, as well as near Houna and 'Ihibodaux in the South Central District. St. Charles Parish is beginning to feel the same pressure as urban expansion from the New Orleans Metropolitan Area spills over into the parish. It is expected that when the new Luling bridge across the Mississippi River connecting up with I-10, U. S. 61, and the soon to be widened Highway 90 is completed, New Orleans and Jefferson Parish resi- dents wishing to relocate in St. Charles Parish will have easy access and hasten the demise of the agricultural area of St. Charles Parish. Agriculture Versus Industrial and Comwrcial Land Uses Another pressure on agriculture land uses is that of industrial development. Chapter 3 of Part II of this report outlined the tremendous expansion of the oil and gas exploration, stripping, refining and storage areas within the South Central District since World War II. Ancillary 177 to that development have been the new petrochemical industries located among what has been called the "Ruhr Valley of the South". All of these industries are interested in cheap water for industrial use and trans- portation. Therefore, they locate near the river on the crests of the natural levees where the good agricultural land used to be. The main concentrations of industry in the South Central District are located along the Mississippi Rver in the parishes of St. Charles, St. John, and St. James. Industry is also concentrated around Houma, Louisiana and along Bayou Lafourche, especially south of the Intracoastal Waterway (see Chapter 3, Part II). Residential Versus Industrial Development Due to the tremendous growth of the region, limited "natural levee" development area, expanding heavy industrial base, and lack of adequate land use controls, conflicts have arisen between residential development and industrial uses in the South Central region. This conflict situation has occurred primarily in the Mississippi River parishes where, often heavy industries such as bulk terminals or chemical plants exist side by side with residential development. Some of the problem listed by residents living near to heavy industry include: 1. Dust, other particulates settling over residential areas from plants, especially bulk storage facilities. 2. Excessive noise from transportation and processing activities at all hours of the day and night. 3. Destruction of residential through streets due to heavy machinery in or near residential areas. 178 4. Regular transportation of dangerous materials in or near residential areas. 5. Air pollution from plants and pollution of waterways with toxic or hazardous wastes. Several accidents with hazardous wastes have been reported and evacuations of residents have been necessary at times during these emergencies. Uneven enforcement of air pollution regulations and occasional dis- regard of these regulations regarding dumping and air emissions have caused numerous complaints. Unfortunately, lack of land use controls such as good zoning laws at the local level have allowed plants to build near or right next to residential areas in the past. Likewise, developers have built subdivi- sions adjacent to existing industries without regard to the consequences. Parishes have recently recognized this problem and are attempting to regulate future industrial and residential growth through the standard methods of land use control available to them. They have also enlisted the State to enforce air quality regulations, and dumping and water pollution programs in the area. The State is developing hazardous waste and solid waste management plans to regulate the transportation and disposal of waste or hazardous substances. These activities and aware- ness of problems should eliminate, or at least minimize future problem in this area. Waste Disposal and Pollution There are currently twenty-three solid waste disposal sites in the South Central District. Table 4.4 lists these sites by Parish. 179 TABLE 4.4 Parish Number of Nuirber of Open Dumps Number with Land Disposal Sanitary Burning Sites Landfills Assumption 2 0 2 0 Lafourche 6 3 3 2 St. Charles 6 4 2 2 St. James 3 0 3 3 St. John 2 1 1 1 Terrebonne 4 0 4 2 Source: Office of Science, Technology and Environmental Policy (1979) page 6. Note: No sanitary landfill within the SCP&DC district met state require- ments as of July 11, 1979. 180 Due to the Federal regulations such as the Federal- Water Pollution Control Act, the Coastal Zone Managemmt Act, and the Resource Conserva- tion and Recovery Act, disposal in wetlands areas (formerly used inten- sively for landfills) is prohibited. As in other uses of man, the natural levee provides the soils and cover necessary to operate a waste disposal site. Thus, there is another competing land use on the natural levee. The State of Louisiana is a1so cracking down on the many illegal open dumps in the region under solid waste management plan, developed in response to the Federal Legislation. Parishes are now being forced to operate stringently controlled waste sites on good natural levee soils. Some problems in disposal of waste in the South Central District are: 1. high cost of land 2. high cost of operating a waste disposal site that meets regulations 3. location of sites away frcm human habitation 4. water pollution from leakout fran improper sites 5. destruction of agricultural land Resource recovery has been investigated as an alternate to land- fills but the population density of the region is not yet high enough to make this method cost effective throughout the region. Hazardous waste is a real problem in an area rich as ours with many petrochemical plants moving highly dangerous chemicals. These too are stored in sites, legal and illegal, across the district. Currently the 181 state, regional planning corrmissions, and paxishes are studying the problem of what to do with the transportation and storage of these wastes, so as not to pollute the environment and/or endanger the health of the general population. Water Pollution This area like others across the country, has had to grapple with the problem of degradation of water quality due to water pollution. Water pollution in our district results from the following sources: 1. out of district sources, principally the Mississippi River 2. pollution from municipal sewerage and drainage water 3. industrial pollution 4. agricultural runoff 5. septic tank effluent 6. pollution from crop The Mississippi River, draining two-thirds of the continental United States, is a major source of water pollution. Most of the dis- trict derives their drinking water from the river either directly or indirectly via pumpage down. Bayou Lafourche industries also use the water in their processes, where it is then discharged back into the system after use. There is currently no parish that has a "parish-wide" sewerage disposal system. Table 4.5 lists the commmities within the south Central District and their current methods of sewerage disposal. Although many areas are served by at least primary sewerage treat- ment, the facilities are often inadequate, outdated and violate Federal or State pollution guidelines. Many areas are still on private 182 TAELE 4. 5 Sewerage Disposal Methods SCP&DC District Public Entity SeweE@@ System Assumption Paxish Septic tanks Gramercy (St. James) Sewerage System Golden Meadow (Lafourche) Septic Tanks Lafourche Parish Septic Tanks Lutcher (St. Jams) Sewerage System Houmia (Terrebonne) Sewerage System Lockport (Lafourche) Sewerage System St. Chaxles Parish Sewerage/Septic Tanks St. John Parish Sewerage/Septic Tanks St. James Parish Sewerage/Septic Tanks Thibodaux (Lafourche) Sewerage System Source: South Central Planning & Development Conmission, (1977) pages 128-142. *Note: Parish data excludes unincorporated miunicipalities. They are treated separately. 183 septic tank disposal system on soils that have a limited capacity to accoamodate them. Some subdivisions have small "package" plants that deal with sewerage with varying degrees of success Currently drainge water from urban (or rural) areas is not being treated. These waters carry septic tank leakage effluent plus all kinds of pollutants washed off of city streets. Industrial and agricultural pollution are an inportant, but dirrdn- ishing problem. Industries discharge mainly into the Mississippi River and are now being regulated. Agricultural pollution is caused by ferti- lizer and pesticide residues in runoff into wetlands. This too is now under regulation and a diminishing problem. Concentration of camps in wetlands areas cause a local health hazard because water flows are low and incapable of handling large volumes of sewerage. Camps often have no sewerage and pollute these areas. The water pollution problems have cleared up considerably with public awareness and money available from the Federal government to help address problem. Sewerage plants have been built and refurbished, industrial effluent has been curtailed on quantity and concentration and regulations have limited "non-point" source discharges such as ferti- lizer or pesticide runoff. WEIIANDS Oil and Gas Exploration/Navigation Activities Negative Effects As mentioned in the section of this Chapter on channelization, oil and gas exploration and development have bad a profound effect on wet- 184 lands. Besides doing ecological damage by causing erosion, loss of wet- lands, destruction of vegetation, etc., to the natural systen, several negative aspects of this activity have hurt man. Channelization of wetlands causes: 1. vegetation destruction causing loss of habitat, nursery area and decreased productivity of ccmmercial and recreational species of animals 2. saltwater intrusion that poisons municipal water supplies 3. water pollution decreasing productivity of commercial and recreational species, and hurting the fishing industry 4. land loss causing increased flood hazards to coastal communi- ties 5. the flooding of waters from hurricanes to reach inland communities quicker and with greater height 6. loss of wetlands causing loss of part of a system that assim ilates pollutants from and can serve as effective sewerage treatment Economic Value of Wetlands If these effects go, they eventually will adversely affect the carmercial fish harvest offshore. Tables 4.6, 4.7, 4.8, 4.9, 4.10, and 4.11 list some of the tremendous productivity of the wetlands for fish and trapping activities. Tables 4.1-2, 4.13 and 4.14 list the total estimated value of wetlands in one Louisiana estuarine basin, to nm. As can easily be seen, wetlands provide tremendous amount of benefits, directly and indirectly to man. 'Iherefore, loss of these lands through channelization adversely affects the econcimic well being of our entire region. 185 TABLE 4.6 Fish And Shellfish Landings And Value For Louisiana 1966-19176 Average Price Total Total Value Per Pound Year Landings (Lbs.) (1977 Dollars) (1977 Dollars) 1966 647,416,500 $ 73,481,772 $ .1135 1967 620,427,500 $ 68,065,284 $ .1097 1968 763,968,600 $ 75,174,510 .0984 1969 1,013,484,600 64,761,666 .0639 1970 1,115,331,700 97,368,457 .0873 1971 1,377,013,051 76,424,224 .0555 1972 1,081,269,660 104,234,395 .0964 1973 1,040,769,832 130,203,683 .1251 1974 1,233,415,909 108,047,234 .0876 1975 1,128,274,979 99,513,853 .0882 1976 1,232,328,343 147,016,771 .1193 Source: National Marine Fisheries Service, 1967-77. 186 TABLE 4. 7 Percentage of Trapping Harvest From Louisiana Wetlands (By Species) Species Percentage Muskrat 99.8 Nutria 99.1 Mink 70.4 Raccoon 71.3 Otter 92.0 Opossun 88.0 Bobcat 42.9 Source: U. S. Army Corps of Engineers, 1977. Mumphrey, et al. (1978). 187 TABLE 4.8 Average Annual Harvest Of Pelts From Louisiana Wetlands (By Species) 1970-1971 Through 1974-1975 Species Average Annual Harvest Muskrat 406,696 Nutria 1,462,075 Mink 22,707 Raccoon 90,007 Otter 5,525 Opossun 16,379 Bobcat 206 Total 2,003,995 Source: U. S. Anny Corps of Engineers, 1977. Mumphrey, et al (1978). 188 TABLE 4.9 Annual Harvest Of Pelts In Louisiana (All Species) 1967-1968 Through 1975-1976 Average Price Estimated Number Per Pelt Total Value Year Of Pelts (1977 Dollars) (1977 Dollars) 1967-68 2,130,473 $ 2.4152 $ 5,145,518.39 1968-69 3,469,040 3.0112 10,445,973.25 1969-70 3,002,043 3.2597 9,785,759.57 1970-71 2,090,761 3.3609 7,026,838.65 1971-72 1,732,682 4.8662 8,431,577.15 1972-73 2,180,332 6.2821 13,697,063.66 1973-74 2,304,916 6.9605 16,043,367.82 1974-75 2,038,379 5.7881 11,798,341.49 1975-76 2,533,500 5.4533 13,815,935.55 Average 2,386,903 $4.5997 10,979,037.73 'Derived by multiplying the average nunber of pelts (2,386,903) by the average price per pelt ($4.59997). Source: Louisiana Wildlife and Fisheries Comnission, 1977. Munphrey, et al, 1978. 189 TAEU 4. 10 Average Annual pounds of Meats Frorn Louisiana Wetlands (By Species) 1970-1971 Through 1974-1975 Species Average Muskrat 279,440 Nutria 9,116,750 Raccoon 376,464 Opossm 146,080 Total 9,918,734 Source: U. S. Army Corps of Engineers, 1977. Mumphrey, et al (1978). 190 TABLE 4. 11 Annual Harvest Of Meats Fran Furbearing Animals In Louisiana (All Species) 1967-1968 Through 1976-1977 Average Price Estimated Number Per Pound Total Value Year Of Pounds (1977 Dollars) (1977 Dollars) 1967-68 91220,000 $ .1667 $ 1,536.974.00 1968-69 11,660,000 .1625 1,894,750.00 1969-70 10,480,000 .1393 1,459,864.00 1970-71 8,770,000 .1324 1,187,628.00 1971-72 8,970,000 .1288 1,155,336.00 1972-73 11,300,000 .1310 1,480,300.00 1973-74 12,550,000 .1486 1,864,930.00 1974-75 10,430,000 .1375 1,434,125.00 1975-76 11,136,000 .1369 1@524,518.40 1976-77 3,635,000 .1883 684,470.50 Average 9,815,100 .1472 1,444,782.72 1 'Derived by multiplying the average nunber of pounds of meats (9,815,100) by the average price per pound (.1472). Source: Louisiana Wildlife and Fisheries Cam-iission, 1977. Mumphrey, et al (1978). 191 TABLE 4.12 Estirmted Gross Economic Contribution Of A Wetland Acre In The Barataria Basin Annual Return Present Value Activity Category Per Acre Per Acre Conmercial Fishing $ 286.36 $ 5,540.42 Non-Conmercial Fishing $ 3.19 46.40 Coamercial Trapping (Pelts & Meats) 11.69 170.05 Recreation: Economic Inpact of Recreation Expenditures 60.08 873.89 Economic Value of User- Benefits from Recreation 104.33 2,428.17 Totals $ 465.65 $ 9,058.93 Source: Mumphrey, et al (1978). 192 TABLE 4.13 Estimated Net Economic Contribution .Of A Wetland Acre In The Barataria Basin Annual Return Present Value Activity Category Per Acre Per Acre Comneercial Fishing $ 26.45 $ 384.73 Camiercial Trapping 1.91 27.84 (Pelts & Meats) Recreation Economic Value of User-Benefits 104.33 2,428.17 Totals $ 132.69 $ 2,840.74 Source: Wurphrey, et al (1978). 193 TABLE 4. 14 Revised Estimate Of Gross Economic Contribution Of A Wetland Acre In The Barataria Basin Based On U. S. Army Corps Of Engineers Regulations Annual Return Present Value Activity Category Per Acre Per Acre Comercial Fishing $ 93.13 $ 1,801.76 Non-Comnercial Fishing 3.19 46.40 Coffne-rcial Trapping 3.80 55.30 (Pelts & Meats) Recreation Economic In-pact of Recreation Expenditures 20.58 299.28 Economic Value of User Benefits from Recreation 76.95 1,790.54 Tbtals 197.65 3,993.28 Source: MLwphrey, et al (1978). 194 Mitigation Efforts As mentioned previously much of the environmental damage has been done in the past. Currently, the technology exists to minimize damage to the wetlands. The State of Louisiana has an approved Coastal Zone Management Program which fosters local supervision of many wetland activities. This marks the first time that local governments in our area have participated in, or planned for managing the wetlands resources within their borders. These efforts, combined with U. S. Amy Corps of Engineers 404 dredge and fill permit system and the Federal 208 and 201 water pollution control plans of the State should help mitigate future damage to these areas. Economic factors and regulations also make reclamation a dubious if not impossible proposition. This will help slow down wetland deter- ioration. One economic loss to the parish often overlooked is that of the severance tax from wetland oil and gas extraction. Once an area erodes away, the water bottom becomes state owned so that the parish loses its allotment of tax revenues from that former tract of wetlands. By,con- trolling reclamation and channelization of wetlands, the parishes and State can slow down land loss and help preserve a vital source of local revenue. 195 Stopping Land Loss Several methods have been proposed for pursuing active policies aimed at slowing or actually stopping land loss. Such methods include the following: 1. allowing the river to resume its natural patterns of flooding and silt deposition 2. controlled introduction of freshwater to combat saltwater intrusion and reintroduce nutrients into the system 3. controlled introduction of water and silt to rebuild subsiding, eroding areas (Gagliano, et al, 1973) Of course the first alternative is unacceptable, due to the fact that human habitation could not exist here as we know it under these circumstances. Alternative t@m is currently being used in St. Bernard Paxish and contemplated in Jefferson Parish to reintroduce significant quantities of freshwater back into the ecosystem. Alternative three is the best, but costliest of the tV.Q feasible alternatives. Maintaining a channel depth and flow to more large amounts of silt vould be expensive and dangerous to the flood protection system that such a distribution system would have to break. ODNCLUSIONI An attempt has been made here in this chapter to condense and present some of the most iffiportant,conflicts and land use problems in our region. Much has been written about these problem and many have no viable solution at the present time. In Phase II of our Land Use report, 196 i we will statistically assess these and other conflicts through a study of land use pattern changes over time. It is hopeful that the reader will gain a better understanding of the issues that confront this area regarding the utilization of our mst previous resource, the land we live on. 197 BIBLIOGRAPHY Craig, N. and Day, J. (1976) Cumulative Irrpact: Effects of Eutrophication and Salinity Changes in the Nursery Zone of Barataria Basin. Center for Wetland Resources, Louisiana State University, Baton Rouge, Louisiana. Gagliano, S. M. ((1973) Hydrologic and Geologic Studies of Coastal Louisiana: Report No. 14, Canals, Dredging and Land Reclamation in the Louisiana Coastal Zone. Center for Wetland Resources, Louisiana State University, Baton Rouge, Louisiana. Gagliano, S. M. et al (1973) Hydrologic and Geologic Studies of Coastal Louisiana: R6@@rt No. 18 Volune I: Environmental Atlas and Multi-Use Management Plan for South Central Louisiana. Center for Wetland Resources, Louisiana State University, Baton Rouge, Louisiana. Louisiana Department of Public Works (1974) Official Map of Louisiana. Louisiana Department of Public Works, Baton Rouge, Louisiana. Louisiana Wildlife and Fisheries Commission (1976) Comparative Lakes of F'ur Animals in Louisiana. Louisiana Wildlife and Fisheries Cannission, New Orleans, Louisiana. Amphrey, A. J. et al (1975) Louisiana Metropolitan Wetlands: A Planning Perspective. Urban Studies Institute, University of New Orleans, New Orleans, Louisiana. (Unpublished). Nhunphrey, A. J. et al (1978) The Value of Wetlands in the Barataria Basin. Ur6aiT Tt-udies Institute, University of New Orleans. New Orleans, Louisiana. National Marine Fisheries Service, Natural Oceanic and Atmospheric Administration, U. S. Department of ConTa-erce (1977) Fisheries of the United States: 1976. Washington, D. C., U. S. Government Printing Office. Natural Marine Fisheries Service, National Oceanic and Atnospheric Administration, U. S. Department of Connxerce (1967-77) Louisiana Landings. U. S. Government Printing Office, Washington', D. C. Office of Science, Technology and Environmental Policy (1979) Preliminary List of Open Dumps. Office of Science, Technology and Environmental Policy, Baton Rouge, Louisiana. South Central Planning and Development Commission (1977) Overall Economic Development Program. South Central Planning and Developn-ent Comnission, 'Ihibo Louisiana. 198 U. S. Army Cc)rps of Engineers (1970) Levees on the Lower Mississippi. Department of the AnW, Mississippi River Conmission, Corps of Engineers, Vicksburg, Mississippi. U. S. Amy Corps of Engineers (1973) Flood Central: Lower Mississippi River Valley. U. S. A:rmy Corps of Engineers, Vicksburg, Mississippi. U. S. Army Cc)rps of Engineers (1977) Value of Wetlands and Bottcmland Hardwoods. New Orleans, Louisiana, U. S. Army Corps of Engineers. 199 DATE DUE GAYLORDINo. 2333 @ Tkil