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    Claude E. Boyd

    School of Fisheries, Aquaculture and Aquatic Sciences

    Auburn University, Alabama 36849 USA

    The Theory and Practice of Shrimp PondBottom Soil Management

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    Basic Soil Science Concepts for

    Aquaculture

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    Holds pond water (not water quality issue)

    Accumulates sediment

    Exchanges cations with water

    Removes phosphorus from water

    Source of combined nitrogen to water

    Removes oxygen from water column

    Source of potentially toxic microbial metabolites

    Soil acidity neutralizes alkalinity in water

    Source of nutrients in water via dissolution ofminerals

    Habitat for benthic food organisms

    Harbors pathogens

    Role of Pond Soil

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    Soil triangle. To use, mark percentage clay and percentage sand on the

    appropriate axes. From these points, project a line inward from the

    clay axis and parallel to the sand axis and another line from the sand

    axis parallel to the silt axis. The interaction of the two projected lines

    will denote soil texture.

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    Pond on Sandy Soil

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    Turbid Water Supply

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    Pond Filled with Sediment

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    Average rate of sediment accumulation isroughly 1.0 cm/yr, but is much faster during the

    first 2 or 3 years that a pond is used.

    Sediment accumulates forming a unique profile

    with distinct horizonsupper 4 or 5 cm effects

    water quality.

    Heavy mechanical aeration may greatly

    accelerate erosion.

    Comments on Sedimentation

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    HORIZONS IN SEDIMENT PROFILE

    FLOCCULENT LAYER

    MIXED

    SEDIMENT

    LAYER

    Oxidized (aerobic)

    Reduced

    (anaerobic)

    MATURE STABLE

    SEDIMENT

    TRANSITIONAL

    LAYER

    ORIGINAL, UNDISTURBED

    POND BOTTOM

    PO

    ND

    SOILPROFILE

    WATER HORIZON CHARACTERISTICS

    F

    S

    M

    T

    P

    Water with high concentration of mineral

    and organic solids, aerobic

    Sediment with high water content and

    low dry bulk density, abundant organic

    matter, well stirred by physical and

    biological agents, thin aerobic surface

    but anaerobic below

    Sediment with medium water content

    and intermediate dry bulk density,

    abundant organic matter, not stirred,

    anaerobic

    Transition between M and P horizonswith characteristics intermediate

    between M and P horizons, not stirred,

    anaerobic

    Low water content and high bulk

    density, usually compacted, low organic

    matter, not stirred, anaerobic

    }So

    Sr

    }MT

    PT

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    Brown Oxidized soil

    Black Reduced soil underneath

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    Aerobic Saprophytic

    MicroorganismsThese organisms use oxygen in

    respiration to decompose organic

    matter to carbon dioxide, mineralnutrients, and water. The typical

    equation for aerobic decomposition is:

    Organic Matter + O2 CO2+ H2O + Mineral

    Nutrients

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    Fermentation

    When anaerobic conditions exist, some

    organisms can use intermediate organic

    metabolites as electron acceptors. An

    example of a fermentation reaction is:

    C6H12O6 2CH3CH2OH + 2CO2

    Also, can have end products such as

    formate, propionate, lactate, etc.

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    Denitrification

    Some bacteria can use oxygen from

    nitrate when no dissolved oxygen is

    available as illustrated by the followingreaction:

    6NO3-

    + 5CH3OH 5CO2+ 3N2+ 7H2O +6OH-

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    Reduction of Ferric Hydroxide and

    Manganese Oxide

    Some bacteria can derive oxygen from

    iron and manganese compounds.

    CH3COOH + 2H2O 2CO2+ 8H+

    Fe(OH)3+ 3H+ = Fe2++ 3H

    2O

    MnO2+ 4H+= Mn2++ 2H2O

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    Sulfate Reduction

    Sulfate-reducing bacteria use

    sulfate as an oxygen source asshown below:

    SO42-+ 4H+ S2-+ 4H2O

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    Methane Bacteria

    Methane-producing bacteria use

    oxygen from carbon dioxide asillustrated in the following

    equation:

    8H++ CO2 CH4+ 2H2O

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    Date

    7/05 9/05 11/05 1/06 3/06 5/06

    P

    otassium

    (mg/L)

    0

    10

    20

    30

    40

    50

    60

    70First treatment

    Second treatment

    Third treatment

    Changes in potassium concentration following three potassium

    additions of 50 mg/L each in laboratory soil-water systems.

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    Potassium loss from water and adsorption by soil

    over 8 months in laboratory soil-water systems with

    56 L of water and 9.6 kg soil.

    Variable Average

    Potassium loss from water

    (mg/L) 89

    (mg/tank) 4,982

    Exchangeable potassium adsorption by soil

    (mg/kg) 136

    (mg/tank) 1,284Potassium fixed by nonexchange process

    (mg/kg) 390

    (mg/tank) 3,568

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    Number of Consecutive Exposures

    0 2 4 6 8 10 12 14

    Potass

    ium

    adsorbedbyso

    il(mg/kg)

    0

    100

    200

    300

    400

    500

    Potassium adsorption by samples of original pondsoil from an inland shrimp farm in Alabama.

    Samples were exposed twelve consecutive times to

    50 mg/L potassium (potassium chloride in distilled

    water) in a shaker trial.

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    Soil is source of substances to water viadissolution of minerals. Possibly, most

    important are carbonate and silicate minerals

    that dissolve to give alkalinity as illustrated with

    calcium carbonate and silicate:

    CaCO3+ CO2+ H2O Ca2++ 2HCO3

    CaSiO3+ 2CO2+ 3H2O Ca2++ 2HCO3-+ H4SiO4.

    Dissolution of Minerals

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    Neutralization of Exchangeable Acidity in Soils

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    Mangroves

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    Mangrove Soil

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    Pyrite Formation

    2CH2O + SO42- H2S + 2HCO3

    Fe(OH)2+ H2S FeS + 2H2O

    FeS + S FeS2

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    Pyrite Oxidation

    FeS2+ 3.75O2+ 3.5H2O Fe(OH)3+ 2SO42-

    + 4H+