1.0 Intended Use <strong>of</strong> <strong>Guidance</strong> DocumentThis guidance document is designed to help the person responsible for conductingremediation comply with the <strong>New</strong> <strong>Jersey</strong> Department <strong>of</strong> Environmental Protection’srequirements established by the <strong>Technical</strong> Requirements for Site Remediation (<strong>Technical</strong>Rules), N.J.A.C. 7:26E. This guidance will be used by many people involved in theremediation <strong>of</strong> a contaminated site including Licensed Site Remediation Pr<strong>of</strong>essionals(LSRP), environmental consultants, and other environmental pr<strong>of</strong>essionals. Because therewill be many users, the generic term “investigator” will be used to refer to anyremediating party or person who uses this guidance to remediate a contaminated site onbehalf <strong>of</strong> a remediating party.The procedures for a person to vary from the technical requirements in regulations areoutlined in the <strong>Technical</strong> Rules at N.J.A.C. 7:26E-1.7. Variances from a technicalrequirement or deviation from guidance must be documented and adequately supportedwith data or other information. In applying technical guidance, the NJDEP recognizesthat pr<strong>of</strong>essional judgment may result in a range <strong>of</strong> interpretations on the application <strong>of</strong>the guidance to site conditions. This guidance was prepared in accordance with the<strong>Technical</strong> Requirements for Site Remediation, N.J.A.C. 7:26E, the Site RemediationReform Act, N.J.S.A. 58:C-1 et seq. and the Administrative Requirements for theRemediation <strong>of</strong> Contaminated Sites, N.J.A.C. 7:26C.This guidance supersedes all previous NJDEP guidance issued on this topic.This guidance was prepared with stakeholder input. The committee responsible for thepreparation <strong>of</strong> this document was composed <strong>of</strong> the following people: Nancy Hamill,Chair (NJDEP), Greg Neumann (NJDEP), Allan S. Motter (NJDEP), Charles Harman(AMEC Earth & Environmental), Ralph Stahl (E.I. duPont and Company), and KariAnneCzajkowski (Langan Engineering & Environmental Services). The committee wishes toacknowledge the contributions <strong>of</strong> the following individuals: Daniel Cooke (AMEC Earth& Environmental), Christina Faust (SAIC), and Steven Byrnes (NJDEP).2.0 PurposeThe purpose <strong>of</strong> this document is to provide efficient and streamlined tiered guidance forthe evaluation <strong>of</strong> ecological risk in aquatic and terrestrial habitats associated withcontaminated sites. As per N.J.S.A 58:10 B-12 (Brownfields and Contaminated SiteRemediation Act), the guidance will enable users to determine remediation standardsprotective <strong>of</strong> the environment on a case-by-case basis in accordance with guidance andregulations <strong>of</strong> the United <strong>State</strong>s Environmental Protection Agency (USEPA). Thisguidance supplements and provides details for the implementation <strong>of</strong> N.J.A.C. 7:26E andis in accordance with USEPA (1997a), <strong>Ecological</strong> Risk Assessment <strong>Guidance</strong> forSuperfund, Process for Designing and Conducting <strong>Ecological</strong> Risk Assessments, EPA540-R-97-006, Office <strong>of</strong> Solid Waste and Emergency Response, Washington, DC(ERAGS), available at http://www.epa.gov/oswer/riskassessment/ecorisk/ecorisk.htm.<strong>Ecological</strong> <strong>Evaluation</strong>s (EE) and <strong>Ecological</strong> Risk Assessments (ERA) are conducted todetermine whether remedial actions are required in environmentally sensitive naturalresources (ESNR) associated with contaminated sites and to provide the means todetermine ecological risk-based remediation goals. ESNRs are defined as<strong>Ecological</strong> <strong>Evaluation</strong> <strong>Technical</strong> <strong>Guidance</strong> Document 7Version 1.2 8/29/12
environmentally sensitive areas pursuant to the Discharge <strong>of</strong> Petroleum and OtherHazardous Substances, N.J.A.C. 7:1E-1.8, available athttp://www.nj.gov/dep/rpp/brp/dp/downloads/NJAC_7_1E.pdf, and Pinelands pursuantto N.J.S.A.13:18A-1 et seq. and N.J.A.C. 7:50, available athttp://www.state.nj.us/pinelands/images/pdf%20files/pinelandsprotectionact1.pdf.EEs are required for all contaminated sites pursuant to N.J.A.C.7:26E 1.16 Receptor<strong>Evaluation</strong> and N.J.A.C. 7:26E-4.8(a) and 4.8(b) Remedial Investigation <strong>of</strong> <strong>Ecological</strong>Receptors. If the EE indicates that additional ecological investigation is necessary, thenan ERA is required pursuant to N.J.A.C. 7:26E-4.8(c), Remedial Investigation <strong>of</strong><strong>Ecological</strong> Receptors. EEs must be conducted by a person experienced in the use <strong>of</strong>techniques and methodologies for conducting ERAs (C.58:10C-16 (c)). For new cases(initiated remediation after November 4, 2009) or existing cases (initiated remediationbefore November 4, 2009) that have opted into the LSRP program, or after May 2012, theinvestigator may either: (1) be an LSRP, (2) be directly overseen and supervised by anLSRP, or (3) have the EE reviewed and accepted by an LSRP.3.0 Document OverviewThis document provides technical guidance on how to conduct an <strong>Ecological</strong> <strong>Evaluation</strong>(EE) and an <strong>Ecological</strong> Risk Assessment (ERA) pursuant to N.J.A.C. 7:26E-1.16andN.J.A.C. 7:26E-4.8 in environmentally sensitive natural resources (ESNR) associatedwith contaminated sites. <strong>Guidance</strong> is also provided for the derivation <strong>of</strong> site-specificecological risk-based remediation goals, determination <strong>of</strong> Risk Management Decisions(RMD), preparation <strong>of</strong> the EE and ERA reports, management <strong>of</strong> special circumstances,and implementation <strong>of</strong> required data quality assurance and quality control (QA/QC)measures as per N.J.A.C. 7:26E-2.The guidance first describes how to conduct an EE, which is initiated during the SiteInvestigation (SI) pursuant to N.J.A.C. 7:26E-1.16. The EE is conducted to examine thesite for the co-occurrence <strong>of</strong> the following:(1) ESNRs on, adjacent to, or potentially impacted by the site;(2) the presence <strong>of</strong> Contaminants <strong>of</strong> Potential <strong>Ecological</strong> Concern (COPEC) at thesite or area <strong>of</strong> concern (AOC) and in the ESNRs (e.g., contaminants withconcentrations in excess <strong>of</strong> aquatic Surface Water Quality Standards (SWQS) orecological screening criteria (ESC)); and(3) the presence <strong>of</strong> a contaminant migration pathway (historic or current) from thesite to the ESNR or evidence <strong>of</strong> contaminated material having been placeddirectly into an ESNR. As part <strong>of</strong> the SI, an EE must be performed within theregulatory time frame <strong>of</strong> one year from the initiation <strong>of</strong> remediation (N.J.A.C.7:26C-3.2). The mandatory time frame associated with this requirement is twoyears from the initiation <strong>of</strong> remediation (N.J.A.C. 7:26C-3.3). The outcome <strong>of</strong>the EE will be a recommendation either to conduct an ERA or to not conduct anyfurther ecological evaluation.<strong>Guidance</strong> is then provided on how to conduct the ERA, a component <strong>of</strong> the RemedialInvestigation (RI) pursuant to N.J.A.C. 7:26E-4.8. The ERA is a quantitative assessment<strong>of</strong> the actual or potential impacts <strong>of</strong> COPECs from a contaminated site on ecological<strong>Ecological</strong> <strong>Evaluation</strong> <strong>Technical</strong> <strong>Guidance</strong> Document 8Version 1.2 8/29/12
- Page 1 and 2: Ecological EvaluationTechnical Guid
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elatively sedentary organisms that
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COPECs. The following references ar
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tests (USEPA, 2002e). After collect
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multiple reference area soils repre
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In ERAs, tissue residue analyses ar
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Objectives of the ERA: including a
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evaluation might necessitate the co
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N.J.A.C. 7:26E-4.8(c)1. The ERA may
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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