2. Collect a minimum <strong>of</strong> one surface water and sediment sample at eachinflow and outflow area; and3. Collect a minimum <strong>of</strong> one surface water and sediment sample at eachdepositional area where sediments may be expected to accumulate.B. Flowing water areas (e.g., rivers, streams, creeks, wetlands, culverts, andswales) should be sampled as follows: Collect a minimum <strong>of</strong> onesediment sample where sediments are expected to accumulate and aminimum <strong>of</strong> one surface-water sample under low flow (base flow) andhigh flow conditions as follows:1. Collect a minimum <strong>of</strong> one surface-water and one sediment sample upstream <strong>of</strong> the point or area <strong>of</strong> discharge;2. Collect a minimum <strong>of</strong> one surface-water and one sediment sample downstream <strong>of</strong> the point or area <strong>of</strong> discharge; and3. Collect a minimum <strong>of</strong> one surface-water and one sediment sample at thepoint or area <strong>of</strong> discharge.A commonly used approach to locating sediment samples is as follows: Thestream location adjacent to the contaminated site most likely to receivecontaminant input via the contaminant migration pathway is considered theinitial sample point. The study region is divided into linear segments andsample transects are located systematically within each segment; the length<strong>of</strong> the segments and distance between transects increases with increasingdistance downstream. This approach is depicted in Figure 5-1, a diagram <strong>of</strong>a sampling plan indicating 15 sediment samples per segment region. In thisexample, the first segment is from zero to one km, the second from one tothree km, and third from three to seven km. The sampling transects(indicated by dashed lines) are located at 1/4, 1/2, and 3/4 the distance alongeach segment. Sample points (indicated by five dots) are located along thetransects at 1/6, 1/3, 1/2, 2/3, and 5/6 the distance bank to bank (USEPA,1985a). The distance from bank to bank is measured from the mean highwatermark.If a potential for sediment deposition exists, then samples should also becollected from the surrounding floodplain. The actual number and location<strong>of</strong> sample points will be decided on a case-by-case basis, based on the studyobjectives, water-body dimensions, flow conditions, substrate conditions,availability <strong>of</strong> previous data, etc.<strong>Ecological</strong> <strong>Evaluation</strong> <strong>Technical</strong> <strong>Guidance</strong> Document 23Version 1.2 8/29/12
71 0Sampling pointsSampling transectsFigure 5-1: Sketch map <strong>of</strong> river showing stratified regions and sampling points.C. Tidal water areas (e.g., rivers, streams, creeks, wetlands, culverts, andswales) should be sampled as follows. Collect a minimum <strong>of</strong> onesediment sample where sediments are expected to accumulate and aminimum <strong>of</strong> one surface water sample under low and high tideconditions as follows:1. Collect a minimum <strong>of</strong> one surface-water and one sediment sample upstream <strong>of</strong> the point or area <strong>of</strong> discharge;2. Collect a minimum <strong>of</strong> one surface-water and one sediment sample downstream <strong>of</strong> the point or area <strong>of</strong> discharge;3. Collect a minimum <strong>of</strong> one surface-water and one sediment sample at thepoint or area <strong>of</strong> discharge; and4. If a potential for sediment deposition exists, then samples should also becollected from the surrounding floodplain.II. WetlandsWetlands (e.g., emergent, shrub-scrub and forested) should be sampled asfollows:A. Collect a minimum <strong>of</strong> one surface-water (if present) and one sedimentsample at the point or area <strong>of</strong> discharge;B. Collect a minimum <strong>of</strong> one surface-water and one sediment sampledowngradient <strong>of</strong> the point or area <strong>of</strong> discharge; andC. Collect a minimum <strong>of</strong> one surface-water and one sediment sample at adepression or depositional area within the wetland.III. UplandsUpland areas containing ESNRs should be sampled as follows:A. Collect a minimum <strong>of</strong> one soil sample at the point or area <strong>of</strong> discharge;<strong>Ecological</strong> <strong>Evaluation</strong> <strong>Technical</strong> <strong>Guidance</strong> Document 24Version 1.2 8/29/12
- Page 1 and 2: Ecological EvaluationTechnical Guid
- Page 3 and 4: 6.2.1.3 Biological Sampling of Fish
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- Page 7 and 8: Executive SummaryThis document prov
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sediment (i.e., that fraction that
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Twelve dioxin-like PCB congeners ha
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indicates burial of potential dioxi
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of evidence for evaluating risk unt
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7.2.1 Apparent Effects Threshold Ap
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when site conditions are most simil
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destroying 10 acres of the mature f
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ASTM (American Society for Testing
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Establishing Sediment Quality Crite
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N.J.A.C. (New Jersey Administrative
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USEPA. 1989c. Risk Assessment Guida
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http://www.epa.gov/owow/oceans/regu
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USEPA 2006a. Data Quality Assessmen
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Appendix A - Habitat Survey FormsEc
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Ecological Evaluation Technical Gui
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Appendix B - Sampling Procedures fo
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Appendix C - Surface Water Toxicity
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Short-term chronic studies, endpoin
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Appendix D - Sediment Toxicity Test
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Toxicity Test DesignSediment toxici
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Appendix E - Sediment Pore Water an
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The seven-day daphnid survival and
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esults are then evaluated using USE
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Surber or Square-foot BottomThis sa
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Appendix H - Soil Toxicity TestingS
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another sample may still have a sub
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conservative approach from an ecolo
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Data PresentationTabular presentati