Rules & Regulations of the State of Tennessee
Title 0400 - Environment and Conservation
Subtitle 0400-15 - Division of Remediation
Chapter 0400-15-01 - Hazardous Substance Remedial Action
Section 0400-15-01-.08 - REMEDIATION GOALS
Current through September 24, 2024
(1) Purpose and Objectives
The purpose of this rule is to provide remediation goals for hazardous substance remediation under Chapter 0400-15-01.
The objective of this rule is to develop consistent procedures for the development and usage of remediation goals.
(2) General
These rules provide two basic approaches for establishment of preliminary remediation goals associated with the remedial investigation in part (2)(a)2 of Rule 0400-15-01-.09. These approaches include the determination of Applicable or Relevant and Appropriate Requirements (ARARs) and Background Concentrations. Preliminary remediation goals may be used to determine whether the Department currently considers a specific concentration of a contaminant as an unreasonable risk to public health, safety, or the environment (e.g., water quality criteria based on protection of aquatic organisms in surface water) or to help evaluate whether an exposure pathway for a specific contaminant is of concern (e.g., whether a specific concentration of a contaminant in soil has potential to leach to ground water). Preliminary remediation goals developed through the review of ARARs and background concentrations may be used to determine if the concentrations of hazardous substances are a regulatory concern, or as remediation goals for interim actions. If a Feasibility Study is required for the evaluation of alternative clean-up actions under paragraph (3) of Rule 0400-15-01-.09, then a risk assessment as specified in paragraph (5) of this rule is to be included in the feasibility study. The detail of the risk assessment shall be commensurate to the potential exposure and risk to human health and the environment. These rules allow for final remediation goals to be established, subject to Department approval, using either ARARs, background concentrations, a site-specific risk assessment or a combination of ARARs, background concentrations, and a site specific risk assessment.
(3) Applicable or Relevant and Appropriate Requirements (ARARs)
Responsible parties shall perform a survey to identify all Applicable or Relevant and Appropriate Requirements (ARARs). ARARs are categorized as follows:
These requirements define acceptable levels of hazardous substances for remediation planning purposes. Advisories, criteria, guidance, rules, or laws specified by the Department and the following shall be evaluated for applicability as chemical specific requirements. Where several chemical specific ARARs exist for the same compound by media, the ARARs with the smallest concentration shall apply.
Reserved.
Reserved.
Location specific requirements set restrictions on activities within specific locations such as flood plains or wetlands.
Action specific requirements set restrictions for particular treatment and disposal activities.
(4) Background Concentrations
Responsible parties shall establish background concentrations of the contaminants at the site. Background contaminant levels for the media of concern must be determined in a similar area, in close proximity, and, to the extent possible, in an area unaffected by a site or contamination. This background may be a natural background in relatively non-industrialized or non-commercial areas or control background in industrialized or commercial areas where natural background concentrations are not attainable due to long term industrial or commercial activities. Where background concentrations protect public health, safety, and the environment, remediation goals will not be established by the Department less than the corresponding natural background or control background levels. If the Department has reason to suspect background concentrations do not protect public health, safety, and the environment, the Department may require the liable party to assess the risk posed by background concentrations of the hazardous substance.
(5) Risk Assessment
Responsible parties shall propose for Departmental evaluation remediation goals based on human health and environmental risk assessment included in the feasibility study required in paragraph (3) of Rule 0400-15-01-.09.
The Human Health and Environmental Risk Assessment Method is a qualitative and quantitative process to characterize the nature and magnitude of risks to public health, safety, and the environment from exposure to hazardous substances, pollutants, or contaminants released from specific sites. This process may also characterize risks to the environment when the weight of evidence indicates that effects other than toxicity are significant.
(6) Combination Approach
Remediation goals may be established by using a combination of approaches in paragraphs (3) through (5) [e.g., using MCL's for the ground water remediation goal and utilizing the human health and environmental risk assessment approach or the background approach to determine soil remediation goals.]
(7) Department Approval
Approval from the Department must be received before site specific standards or site specific remediation goals become effective.
(8) Points of Compliance
The remediation goal must be met at the appropriate points of compliance at the site as established by the Department after affording a liable party the opportunity to provide input and after undergoing a public participation process (e.g., Public Notice). The location of the points of compliance shall be based on factors including but not limited to the nature of the site and surrounding area, site access, and potential or actual points of exposure. The point of compliance for ground water monitoring at former waste management areas shall generally be a vertical surface located at the hydraulically downgradient limit of the former waste management area that extends down into the upper aquifer underlying the site. Certain site conditions will affect the point of compliance for ground water monitoring. This will vary if the site is located in karst terrain, the water table is located at or below the top of bedrock in an area where the contaminants may be migrating in fracture zones or other conduit flow, or dense nonaqueous phase liquids (DNAPL's) are present. In the valley and ridge province migration along geologic strike must be considered in the determination of what is considered hydraulically downgradient. Soils are normally sampled at locations selected because of site history, or actual or potential human exposure, or environmental receptors. Generally, points of compliance for soil shall include all areas which contain contaminants in excess of remediation goals.
Points of compliance different from those required by the Department can be established by a liable party, pending approval by the Department, after undergoing a public participation process.
(9) Containment
The Department recognizes that selected remedial actions may involve containment of hazardous substances. Any hazardous substance left on-site must be contained within a specified area and be protective of human health and the environment. A compliance monitoring program must be designed to insure the long-term integrity of the containment system. Unless otherwise approved by the Department, a ground water monitoring program approved by the Department shall be required for all areas where containment is a remedial action.
(10) Institutional Controls
Unless otherwise approved or determined by the Department, the following shall apply:
(11) CERCLA Liability
Establishment of remediation goals under these rules and subsequent remediation to those goals may not relieve a liable party from liability under CERCLA including, but not limited to, liability under CERCLA §107(a)(4)(c) concerning damages for injury to, destruction of, or loss of natural resources.
Table 8-1
Preliminary Remediation Goals
Chemical/Compound* | Goal |
2,3,7,8-TCDD (dioxin) | 3E-8 |
2,4 D | 0.07 |
2,4,5-TP | 0.05 |
Alachlor | 0.002 |
. | ... |
. | ... |
. | ... |
Aluminum | 0.2** |
Antimony | 0.006 |
Arsenic | 0.05 |
Asbestos | 7 million |
. | fibers/liter |
Atrazine | 0.003 |
Barium | 2.0 |
Benzene | 0.005 |
Beryllium | 0.004 |
Bromodichloromethane (THM) | 0.1 |
Bromoform (THM) | 0.1 |
Cadmium | 0.005 |
Carbofuran | 0.04 |
Carbon tetrachloride | 0.005 |
Chlordane | 0.002 |
Chlorodibromomethane (THM) | 0.1 |
Chloroform (THM) | 0.1 |
Chromium | 0.1 |
Copper | 1.3** |
Cyanide | 0.2 |
Di(2-ethylhexyl)phthalate | 0.006 |
Dichloromethane | 0.005 |
1,2,4-Trichlorobenzene | 0.07 |
1,1,2-Trichloroethane | 0.005 |
Dalapon | 0.2 |
Dinoseb | 0.007 |
Diquat | 0.02 |
Endothall | 0.1 |
Endrin | 0.002 |
Glyphosate | 0.7 |
Hexachlorobenzene | 0.001 |
Hexachlorocyclopentadiene | 0.05 |
Oxamyl (vydate) | 0.2 |
Picloram | 0.5 |
Simazine | 0.004 |
Benzo(a) pyrene | 0.0002 |
Di(2-ethylhexyl)adipate | 0.4 |
Dibromochloropropane (DBCP) | 0.0002 |
Dichlorobenzene o-,m- | 0.6 |
Dichlorobenzene p- | 0.075 |
Dichloroethane (1,2-) | 0.005 |
Dichloroethylene (1,1-) | 0.007 |
Dichloroethylene (cis-1,2-) | 0.07 |
Dichloroethylene (trans-1,2-) | 0.1 |
Dichloropropane (1,2-) | 0.005 |
Ethylbenzene | . |
Ethylene dibromide (EDB) | 0.00005 |
Fluoride | 4.0 |
Heptachlor | 0.0004 |
Heptachlor epoxide | . |
Iron | 0.3 |
Lead | 0.015*** |
Lindane | 0.0002 |
Manganese | 0.05** |
Mercury | 0.002 |
Methoxychlor | 0.04 |
Monochlorobenzene | 0.1 |
Nickel | 0.1 |
Nitrate | 10.0 |
Nitrate and Nitrite (total) | 10.0 |
Nitrite | 1.0 |
Pentachlorophenol | 0.001 |
Polychlorinated biphenyls (PCB's) | 0.0005 |
Selenium | 0.05 |
Silver | 0.1** |
Styrene | 0.1 |
Tetrachloroethylene | 0.005 |
Thallium | 0.002 |
Toluene | 1.0 |
Toxaphene | 0.003 |
Trichloroethane (1,1,1-) | 0.2 |
Trichloroethylene | 0.005 |
Trihalomethanes (total) | 0.1 |
Vinyl chloride | 0.002 |
Xylenes (total) | 10.0 |
Zinc | 5.0** |
* All levels in parts per million and are MCL's unless otherwise noted.
** These are SMCL's.
*** Lead is an action level rather than a MCL.
Authority: T.C.A. §§ 68-212-201 et seq. and 4-5-201 et seq.