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Ecological Evaluation Technical Guidance - State of New Jersey

Ecological Evaluation Technical Guidance - State of New Jersey

Ecological Evaluation Technical Guidance - State of New Jersey

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e present at intervals greater than six inches, sampling at depth alsoshould be considered to evaluate potential future risks from the sediments,particularly if future dredging or scouring is likely to occur. To enhancecomparability <strong>of</strong> the resulting data, the same sediment sampling methodshould be used to collect samples from all <strong>of</strong> the sampling locations withinthe assessment area, whenever practicable. However, the need to collectboth surficial and deeper sediments may preclude this possibility in certaincircumstances.2. Sample VolumesA key factor <strong>of</strong> a given sediment study is the types <strong>of</strong> analyses requiredbecause the analyses will determine the sample mass required and howsamples are processed. The sediment samples that are collected in thefield are likely to be subjected to physical, chemical, and/or biologicaltesting to support the overall sediment assessment program. Therefore,the collection <strong>of</strong> sufficient volumes <strong>of</strong> sediment at each sample location t<strong>of</strong>acilitate the preparation <strong>of</strong> subsamples for toxicity testing and subsamplesfor chemical analysis from a single, homogenized sediment sample needsto be given consideration prior to field implementation when dealing witha study design that includes multiple indicators <strong>of</strong> sediment quality.3. Other Typical ParametersIt is important that conventional parameters receive as much carefulattention, in terms <strong>of</strong> sampling and sample processing procedures, as dothe COPECs or parameters <strong>of</strong> direct interest. Other parameters to considerfor analysis as a means to help interpret chemical, biological, andtoxicological data collected in an ERA at a sediment site include TOC,acid volatile sulfide (AVS), sediment grain size, total solids, ammonia,and total sulfides.4. Sample SizeThe number <strong>of</strong> samples collected directly affects the representativenessand completeness <strong>of</strong> the data for purposes <strong>of</strong> addressing project goals. Ageneral rule <strong>of</strong> thumb is that a greater number <strong>of</strong> samples will yield betterdefinition <strong>of</strong> the areal extent <strong>of</strong> the contamination or toxicity. Theappropriate number <strong>of</strong> samples is generally determined by the size <strong>of</strong> thestudy site, type, and distribution <strong>of</strong> the COPECs being measured,characteristics and homogeneity <strong>of</strong> the sediment, concentrations <strong>of</strong>COPECs likely to be found in the sediments, sample volume requirementsand desired level <strong>of</strong> statistical resolution or precision.B. Reference Area SamplingBasic guidance for background area sampling is provided in Section 5.3.4.This section describes the suggested reference area sampling to be used inmore comprehensive sediment sampling programs. Given that sedimentinvestigations typically include community surveys, toxicity tests, tissueresidue sampling, and bioaccumulation studies, the identification and selection<strong>Ecological</strong> <strong>Evaluation</strong> <strong>Technical</strong> <strong>Guidance</strong> Document 56Version 1.2 8/29/12

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