Bio Remediation of Lead

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    Daniel Henderson, Sean Nugent

    Mentor:

    Dr. F. Ryvkin

    Chemistry Department, Emmanuel College, Boston MA

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    The use of plants for cleaning up contamination of soil,groundwater, surface water and air.

    Proven to be a successful way to decrease the concentration ofsome common pollutants in these sites

    Many laboratory and field tests have demonstrated that plantsand other vegetation can absorb, transform, or contain a variety

    of contaminants, including soft and heavy metals and volatileorganics through absorption and other activity in the root zone.

    Major barrier to the implementation of bioremediation is that it is

    new and not fully developed and there is little regulatoryexperience with it.

    ~

    BACKGROUND

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    Lead is a highly toxic metal,dangerous to children at levelsgreater than 25 g/dL

    Causes behavioral problems,learning disabilities, seizures, slowgrowth, hearing problems, anddeath.

    Lead has a cumulative effect onchildren who are at higher risk forexposure and absorption than adults

    US Standards for leadconcentration:

    -In Soil: 400 ppm-In Paint: 5,000 ppm

    LEAD:

    behavioral problemslearning disabilitiesseizuresreproductive problems (in both men andwomen)

    High blood pressureDigestive problemsNerve disordersMemory problemsMuscle and joint pain

    and even death.Lead is most dangerous concerning thehealth of a child. It can slow growth andcause hearing problems and headachesas well as the same symptoms adults

    suffer from.

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    Arsenic: Disrupts the digestive system

    Liver and kidney damage.

    Can also lead to central and peripheral nervous system disorders.

    Mercury (primarily from methylmercury):Impairs the development of the fetus causing impacts on:

    Cognitive thinkingMemoryAttention

    LanguageFine motor visual and spatial skillsCadmium:

    diarrhea

    muscle crampssalivationsensory disturbancesliver injuryconvulsionsshock and renal failureNauseaVomiting

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    Aquatic organisms may be adversely affected by heavy metals inthe environment.

    The toxicity is largely a function of the water chemistry and sedimentcomposition in the surface water system

    Slightly elevated metal levels in natural waters may cause thefollowing effects in aquatic organisms:

    histological or morphological change in tissues changes in physiology, such as suppression of growth and

    development

    change in biochemistry, such as enzyme activity and blood

    chemistry change in behavior and changes in reproduction

    Research has shown that aquatic plants are not able to successfullyregulate metal uptake, and so the water resource should be managed

    for the protection of fish and invertebrates, in order to ensure aquaticplant survivability.

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    Perennial fresh water flowering plant Widely distributed in tropical and sub-tropical

    regions

    Leaves possess swollen portions that act as floats Extensive root system projects beneath water

    surface

    Under ideal growing conditions the plants form afloating mat that can double in size in two weeks

    Water hyacinth plants have been shown to absorb

    remarkable amounts of pollutants such as cadmium,zinc and arsenic

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    Plants used to decontaminate soilsthrough the process of

    bioremediation must do one ormore of the following :

    take up contaminants from soil

    particles and/or soil liquid into theirroots

    bind the contaminant into their root

    tissue, physically and/or chemically

    transport the contaminant fromtheir roots into growing shoots

    prevent or inhibit the contaminantfrom leaching out of the soil

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    Negative effects of Nutrient Enriched

    Environments on Bioremediation:Bioavailable fraction of metals reduces as a

    result of binding to nutrient anions.

    Competition between metals and nutrientcations for uptake sites results in decreased

    absorption.

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    Positive effects of Nutrient Enriched

    Environments on Bioremediation:Increased nutrients promotes plant growth.

    Plant growth in turn creates an increasing

    number of uptake sites for metals.

    Increased uptake sites for metals increases

    the uptake and concentrations of metals in theplants.

    continued

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    All plants were cultivated in plastic tubs containing artificialpond water

    Lead nitrate was added to the container with the experimentalplants Control plants were not exposed to lead solution At predetermined intervals samples of water and plants were

    removed for analysis Water samples were analyzed for the presence of lead using

    flame atomic absorption (210VG Buck Scientific Model) Plants were divided into separate root and leaf samples Root and leaf samples were oven dried, weighed and extracted

    by boiling in a cocktail of nitric and hydrochloric acid After filtration, the extracts were analyzed in the same fashion

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    Lead Stems vs. Lead Control

    0

    0.5

    1

    1.5

    2

    2.5

    3

    Day 0 Day 2 Day 5

    ppm Lead Stems

    Control Stems

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    0

    2

    4

    6

    8

    10

    12

    [Pb](ppm

    )

    Day 1 Day 2

    Plant with Lead vs. Control

    Control Plant roots w ith Lead

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    Data shows that water hyacinth plants effectively remove lead fromsolution. The water hyacinth plant works as a bioaccumulator,drawing heavy metal ions in solution into the roots and up through

    the stem and stolons, leaves, etc. Within five days there was overfour times less lead in the water than there was in the plant roots,and the data from Day 5 samples (both roots and stems exposed to2ppm Lead) suggest the mechanics of lead uptake. The lead ions

    are drawn up via diffusion into the plant roots and up the stem andleaf systems.

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    Determine how the nutrient levels effect the

    absorption levels of the water hyacinth, andinvestigate the ion selectivity of the waterhyacinth in the uptake of heavy metals

    Investigate nutrients such as potassium, nitrates,and phosphates for their individual effect on thewater hyacinths uptake of heavy metals such as

    lead and cadmium.

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    We would like to express our deepest gratitude to ourfaculty mentors for encouragement, patience, andconstant support of this research project.

    We are also grateful to Sharon Patris for initiating theproject, and to Eric Camire and Laura Graziano forassisting.