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1
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- Ken MacGillivray
- Committee Members:
- Dr. Stephen A. Skrabal
- Dr. Robert J. Kieber
- Dr. Robert Whitehead
- University of North Carolina at Wilmington
- 5 September, 2002
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2
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- Can be toxic to biota
- Non-toxic at low conc.’s
- Ubiquitous
- Numerous anthropogenic sources
- Toxicity, bioavailability controlled by speciation
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3
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- Mixing zone between ocean and river
- Interface between fresh and saline systems
- Unique chemistry
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4
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5
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- Cu in the estuary: >99.9%
occurs as Cu-L
- Zn in the estuary: 1-95% occurs
as Zn-L
- Therefore, characterization of ligands crucial to understanding
chemistry of Cu and Zn
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6
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- “Benthic” = bottom of estuary
- Sediments can be important
sources or sinks for ligands, metals
- “Flux” = rate at which
concentration of substance increases or decreases across sediment-water
interface per m2
- Flux: measured in nmol
- m2d
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7
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8
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- Streblospio benedicti:
- a polychaete that is common in
the CFE
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9
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10
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11
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12
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- Burrowing animal
- Can quickly rearrange sediment surfaces
- Hearty, opportunistic organism
- Normal density: 2,000 individuals per m2
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- Determine TDCu, TDZn, and their
fluxes
- Determine Speciation of Cu, Zn and ligand fluxes
- Characterize ligands (Find K’, classes)
- Effect of bioturbation on fluxes
- Significance of benthic fluxes to overlying water of estuary
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14
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- SAMPLING
- Collect with box corer (APRIL and JUNE, 2001)
- Transfer to core tubes
- Sample, Incubate 48-60 hours, Sample
- ANALYTICAL
- Electrochemical Analysis
- Total Dissolved Cu and T.D. Zn – Std. Additions
- Speciation: CLE-CSV
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15
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16
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17
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18
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19
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20
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21
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22
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23
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24
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25
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26
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27
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28
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29
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