Man-made habitat is excluded from sampling for background contaminantlevel purposes. Background area locations with comparable habitat,community structure and maturity, and the same soil type and lithology as thestudy area are preferable. Because <strong>of</strong> soil heterogeneity, at a minimum,several background area samples are strongly recommended to establish arange <strong>of</strong> background contaminant levels. At a minimum, background areasamples should receive the same chemical analyses as site-related samples tomake direct comparisons with the data.For more detailed guidance on biota sampling approaches, techniques, andtissue residue analytical methods, the investigator is referred to the literature(e.g., USEPA, 1994a and 1997a; and ASTM, 2004).6.2.3.5 Surface Soil Toxicity TestsWhen surface soil analytical data exceed the soil criteria listed in the NJDEPESC Table, soil toxicity tests can provide an indication <strong>of</strong> potential effects onsoil invertebrates and plants.Populations <strong>of</strong> soil organisms (e.g., invertebrates and plants) can be impactedwhen the quality <strong>of</strong> the soil in which they live is changed. The magnitude <strong>of</strong>the impact depends on the magnitude <strong>of</strong> the change to either physicalparameters (e.g., Eh/pH, grain size, total organic matter) or chemicalparameters (e.g., concentrations <strong>of</strong> salts, nutrients, and chemicals). Soiltoxicity testing is used to measure the effects <strong>of</strong> these changes on soilorganism survival, growth, or reproduction using a standardized suite <strong>of</strong>laboratory organisms (e.g., earthworms and plants), following standardizedtesting protocols.Soil toxicity tests should follow established guidance as published byAmerican Society for Testing and Materials (ASTM), Standard Guide forConducting Laboratory Soil Toxicity or Bioaccumulation Tests with theLumbricid Earthworm Eisenia Fetida and the Enchytraeid PotwormEnchytraeus albidus (ASTM, 2004), and Standard Guide for ConductingTerrestrial Plant Toxicity Tests (ASTM, 2009).Detailed specifics regarding soil toxicity test procedures can be found inAppendix H.6.3 <strong>Ecological</strong> Risk Assessment ReportUpon completion <strong>of</strong> the ERA, the investigator should document the findings andconclusions in a concise report for review and acceptance by the LSRP. The ERAshould outline the process followed in completing the ERA, and the data collected, insupport <strong>of</strong> its development. The investigator should employ a weight-<strong>of</strong>-evidenceapproach in outlining what the potential ecological impacts associated with identifiedreleases in the site-related ESNRs may be. The investigator, at a minimum, shouldincorporate the following information into the report: Executive Summary: providing a summary description <strong>of</strong> the basis andbackground <strong>of</strong> the project, and the findings <strong>of</strong> field investigations;<strong>Ecological</strong> <strong>Evaluation</strong> <strong>Technical</strong> <strong>Guidance</strong> Document 67Version 1.2 8/29/12
Objectives <strong>of</strong> the ERA: including a description <strong>of</strong> the work plan, and anydeviations realized as a result <strong>of</strong> project implementation;Problem formulation: including a comprehensive site history and descriptions <strong>of</strong>the ESNRs located on, adjacent to and potentially under the influence <strong>of</strong> the site,identification <strong>of</strong> assessment and measurement endpoints, development <strong>of</strong> ECSM,and identification <strong>of</strong> TRVs and other screening benchmarks;Description <strong>of</strong> field activities: including discussion <strong>of</strong> equipment used, testprotocols, tabular descriptions <strong>of</strong> sample locations and depth;Results <strong>of</strong> the chemical and biological analyses and risk calculations includingtabular results and figures showing ESNRs, sampling locations, date and depthsand analytical results in excess <strong>of</strong> the appropriate ESC and delineation samples bymedia, chemical fraction and area as necessary as per N.J.A.C. 7:26E-1.6(b)6;Uncertainty analysis;Conclusions; andAppendices, containing laboratory analytical data and field logs.6.4 Special CircumstancesThe purpose <strong>of</strong> this section is to augment this guidance for commonly occurringproblematic or scientifically challenging circumstances that are not comprehensivelyaddressed in the ERAGs guidance and that, if not carefully considered in the projectplanning stage, may result in an EE or ERA that is inadequate in scope.6.4.1 WetlandsWetlands are unique and sensitive ecological units. Science has come torecognize that wetlands provide valuable functions in the natural environment.These functions include providing necessary breeding habitat for a variety <strong>of</strong>organisms such as waterfowl, fish, and shellfish; erosion and stormwater floodcontrol; groundwater recharge; and nutrient transport. Wetlands can be found infreshwater, brackish, and saline conditions. They can be found along coasts, inforests, and along rivers or creeks. They can be found anywhere that the saturatedsoil conditions necessary for wetlands development exist.Wetlands are defined as those areas that are inundated or saturated by surfacewater or groundwater at a frequency and duration sufficient to support, and thatunder normal circumstances do support, a prevalence <strong>of</strong> vegetation typicallyadapted for life in saturated conditions. Wetlands generally include swamps,marshes, bogs, and similar areas [33 CFR 323.2 (c)]. The primary governingregulation for freshwater wetlands in the <strong>State</strong> <strong>of</strong> <strong>New</strong> <strong>Jersey</strong> is the <strong>New</strong> <strong>Jersey</strong>Freshwater Wetlands Protection Act (N.J.S.A. 13:9B-1 et seq.) and to a lesserextent, the Water Pollution Control Act, N.J.S.A. 58:10A-1 et seq. The rulesgoverning the implementation <strong>of</strong> the Freshwater Wetlands Protection Act and theWater Pollution Control Act are the <strong>New</strong> <strong>Jersey</strong> Freshwater Wetlands ProtectionAct Rules at N.J.A.C. 7:7A. The primary governing regulation <strong>of</strong> coastalwetlands is the Coastal Zone Management Rules, N.J.A.C.7:7.While the focus <strong>of</strong> this guidance is on the completion <strong>of</strong> ERAs, it is important tounderstand that wetlands are ESNRs that are regulated by the NJDEP. As part <strong>of</strong><strong>Ecological</strong> <strong>Evaluation</strong> <strong>Technical</strong> <strong>Guidance</strong> Document 68Version 1.2 8/29/12
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Ecological EvaluationTechnical Guid
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6.2.1.3 Biological Sampling of Fish
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Acronyms and AbbreviationsADDAETAFA
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Executive SummaryThis document prov
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environmentally sensitive areas pur
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Figure 3-1: Flow diagram to describ
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assessment may also include evaluat
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“Hazard quotient” or “HQ” m
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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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Data PresentationTabular presentati