Bill Text: GA HB248 | 2009-2010 | Regular Session | Introduced

NOTE: There are more recent revisions of this legislation. Read Latest Draft

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Bill Title: Georgia Voluntary Remediation Program Act; enact

Spectrum: Moderate Partisan Bill (Republican 6-1)

Status: (Passed) 2009-06-01 - Effective Date [HB248 Detail]

Download: Georgia-2009-HB248-Introduced.html

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09 LC 25 5412

House Bill 248

By: Representatives Barnard of the 166th, Ehrhart of the 36th, Drenner of the 86th, Everson of the 106th, Reese of the 98th, and others

A BILL TO BE ENTITLED
AN ACT

To amend Article 3 of Chapter 8 of Title 12 of the Official Code of Georgia Annotated, relating to hazardous waste, so as to provide for voluntary and timely investigation and remediation of properties where there have been releases of regulated substances into the environment for the purpose of reducing human and environmental exposure to safe levels; to provide a short title; to provide legislative declarations; to define certain terms; to provide for power and duties of the director of the Environmental Protection Division; to provide criteria for qualifying for a voluntary remediation program; to provide for corrective action; to provide for program standards and policies; to provide for rules and regulations; to repeal conflicting laws; and for other purposes.

BE IT ENACTED BY THE GENERAL ASSEMBLY OF GEORGIA:

SECTION 1.

Article 3 of Chapter 8 of Title 12 of the Official Code of Georgia Annotated, relating to hazardous waste, is amended by adding a new part to read as follows:

"Part 3

12-8-100.

This part shall be known and may be cited as the 'Georgia Voluntary Remediation Program Act.'

12-8-101.

(a) It is declared to be the public policy of the State of Georgia to encourage the voluntary and timely investigation and remediation of properties where there have been releases of regulated substances into the environment for the purpose of reducing human and environmental exposure to safe levels and to ensure the cost-effective allocation of limited resources that fully accomplish the provisions, purposes, standards, and policies of this part.

(b) The General Assembly declares its intent to encourage voluntary and cost-effective investigation and remediation of qualifying properties under this part and that provisions of this part shall apply and take precedence over any conflicting provisions, regulations, or policies existing under Part 2 of this article with regard to any properties properly enrolled in the voluntary remediation program created under this part.

12-8-102.

(a) Unless otherwise provided in this part, the definition of all terms included in Code Sections 12-8-62, 12-8-92, and 12-8-202 shall be applicable to this part.

(b) As used in this part, the term:

(1) 'Cleanup standards' means those rules and regulations adopted by the board pursuant to Code Section 12-8-93.

(2) 'Constituents of concern' means the specific regulated substances that may contribute to unacceptable exposure at a site.

(3) 'Controls' means institutional controls or engineering controls.

(4) 'Engineering controls' means any physical mechanism, device, measure, system, or actions taken at a property that minimize the potential for exposure, control migration or dispersal, or maintain the effectiveness of other remedial actions. Engineering controls may include, without limitation, caps, covers, physical barriers, containment structures, leachate collection systems, ground water or surface water control systems, solidification, stabilization, fixation, slurry walls, vapor control systems, signs, point-of-use treatment, fences, and barrier-like property development features such as pavements, buildings, walls, and other structures.

(5) 'Exposure' means contact of a constituent of concern with a receptor.

(6) 'Exposure domain' means the contaminated geographical area or areas of a site that can result in exposure to a particular receptor by a specified exposure pathway: the soil exposure domain for routine surficial contact with site soils is the soil area impacted by site constituents of concern from the ground surface down to a depth of two feet below ground surface; the soil exposure domain for exposure of construction workers or underground utility workers is the impacted area of site soils from the ground surface down to the depth of construction; and the soil exposure domain for protection of groundwater at an established point of exposure is the impacted area of site soils from the ground surface down to the uppermost groundwater zone.

(7) 'Exposure pathway' means a route by which a receptor comes into contact with a constituent of concern.

(8) 'Fate and transport parameters' means quantitative factors that describe the various media through which constituents of concern migrate from a source of release to a receptor.

(9) 'Institutional controls' means legal or administrative measures that minimize the potential for human exposure to contaminants of concern or protect and enhance the integrity of a remedy or engineering controls. Examples include, without restriction: easements, covenants, deed notices, well drilling or groundwater use prohibitions, zoning restrictions, digging restrictions, orders, building permit conditions, and land-use restrictions.

(10) 'Point of demonstration wells' means monitoring wells located between the source of site groundwater contamination and the actual or estimated downgradient point of exposure.

(11) 'Point of exposure' means the nearest downgradient, three-dimensional location that could reasonably be considered for installation of a drinking water supply well or the location of the nearest drinking water supply well not more than 1,000 feet downgradient from a point of demonstration well.

(12) 'Receptor' means any human or sensitive organism which is or has the reasonable potential to be adversely affected by the release of constituents of concern.

(13) 'Representative concentration' means the average concentration to which a specified receptor is exposed over an appropriate exposure duration within a relevant exposure domain for soils or at an established or estimated point of exposure for groundwater.

(14) 'Voluntary remediation program' means the program established under this part.

(15) 'Voluntary remediation property' means a qualifying property enrolled in the voluntary remediation program.

(16) 'Technical impracticability' means the inability to fully delineate or remediate contamination without incremental expenditures grossly disproportionate to the incremental benefit. An example may include, without limitation, dense non-aqueous phase liquids in fractured bedrock settings.

12-8-103.

The board shall have the power to adopt, promulgate, modify, amend, and repeal rules and regulations to implement and enforce the provisions of this part as necessary to provide for the investigation and remediation of voluntary remediation properties, to the extent necessary to facilitate the accomplishment of the provisions, purposes, standards, and policies of this part.

12-8-104.

(a) The director shall have the power and duty:

(1) To make determinations, in accordance with procedures and criteria enumerated in this part, as to whether a property qualifies and an applicant is eligible for the voluntary remediation program;

(2) To approve, in accordance with procedures and criteria enumerated in this part and rules and regulations promulgated pursuant to this part, conceptual corrective action plans;

(3) To approve, in accordance with procedures and criteria enumerated in this part and rules and regulations promulgated pursuant to this part, compliance status reports;

(4) To concur with certifications of compliance;

(5) To collect application fees from participants;

(6) To compel that reasonable access be granted to affected properties which are demonstrated to have been affected by a release and which are not owned or controlled by the applicant; and

(7) To grant waivers of all or any portion of the fees provided by this part for any small business or for any county, municipality, or other political subdivision of this state.

(b) The powers and duties described in subsection (a) of this Code section may be exercised and performed by the director through such duly authorized agents and employees as the director deems necessary and proper.

12-8-105.

In order to be considered a qualifying property for the voluntary remediation program under this part, a property shall meet the following criteria:

(1) The property must be listed on the inventory under Part 2 of this article or be a property which meets the criteria of Code Section 12-8-205 or otherwise have a release of regulated substances into the environment;

(2) The property shall neither:

(A) Be listed on the federal National Priorities List pursuant to the federal Comprehensive Environmental Response, Compensation, and Liability Act, 42 U.S.C. Section 9601, et seq.; nor

(B) Be currently undergoing response activities required by an order of the regional administrator of the federal Environmental Protection Agency; and

(3) Any lien filed under subsection (e) of Code Section 12-8-96 or subsection (b) of Code Section 12-13-12 against the property shall be satisfied or settled and released by the director pursuant to Code Section 12-8-94 or Code Section 12-13-6.

12-8-106.

(a) In order to enroll any qualifying property in the voluntary remediation program described in this part, an applicant shall submit to the director a conceptual corrective action plan prepared by a registered professional engineer or a registered professional geologist who is registered with the State Board of Registration for Professional Engineers and Land Surveyors or the State Board of Registration for Geologists and who has for a minimum of eight years engaged in the investigation and remediation of releases of regulated substances, including a minimum of four years in responsible charge of the investigation and remediation of such releases. The conceptual corrective plan shall be in such streamlined form as may be prescribed by the director; provided, however, that the plan shall, at minimum, enumerate and describe those actions planned to bring the qualifying property into compliance with the applicable cleanup standards, with one or more registered professionals to be retained by the applicant at its sole cost to oversee the investigation and remediation described in the plan; all in accordance with the provisions, purposes, standards, and policies of the voluntary remediation program. The conceptual corrective action plan shall be considered an application for enrollment in the voluntary remediation program, and a nonrefundable application fee of $3,000.00 shall be submitted with the application.

(b) Upon the director's approval of the conceptual corrective action plan described in subsection (a) of this Code section, the qualifying property shall be deemed enrolled, and the applicant deemed a participant, in the voluntary remediation program. It shall be the responsibility of the participant to cause one or more registered professionals to oversee the implementation of said plan in accordance with the provisions, purposes, standards, and policies of this part. The registered professional shall submit semi-annual status reports to the director describing the implementation of the plan during the preceding period. Upon request of the applicant, the director shall have the discretion to approve annual or longer periods for submittal of status reports. Within 30 days of the director's approval of the conceptual corrective action plan described in subsection (a) of this Code section, the director shall cause the relevant voluntary remediation property to be designated on the inventory under Part 2 of this article as undergoing corrective action pursuant to the voluntary remediation program.

(c) The participant may terminate at any time the enrollment of the property in the voluntary remediation program and the participant's requirements under this part. The director may terminate, at any time prior to approval of the compliance status report described in subsection (a) of this Code section, the enrollment of the property in the voluntary remediation program and the participant's requirements under this part if the director determines that either:

(1) The participant has failed without justification to implement the conceptual corrective action plan in accordance with the provisions, purposes, standards, and policies of the voluntary remediation program; or

(2) Such continued enrollment would result in a condition which poses an imminent threat to human health and the environment.

(d) Upon completion of corrective action under this Code section, the participant shall cause to be prepared a compliance status report confirming consistency of the corrective action with the provisions, purposes, standards, and policies of the voluntary remediation program and certifying the compliance of the relevant voluntary remediation property with the applicable cleanup standards in effect at the time.

(e) Upon receipt of the compliance status report described in subsection (d) of this Code section, a decision of concurrence with the report and certification shall be issued on evidence satisfactory to the director that it is consistent with the provisions, purposes, standards, and policies of the voluntary remediation program. Within 90 days of the director's written concurrence, the director shall cause the property to be removed from the inventory under Part 2 of this article.

(f) In addition to other provisions of this part:

(1) The director shall remove the voluntary remediation property from the inventory at any time that the participant demonstrates to the director, in accordance with rules and regulations promulgated by the board pursuant to Part 2 of this article, that a release exceeding a reportable quantity does not exist at the voluntary remediation property, unless the director issues a decision that such release poses an imminent threat to human health and the environment;

(2) The participant shall not be required to perform corrective action or to certify compliance for groundwater if the voluntary remediation property was listed on the inventory as a result of a release to soil exceeding a reportable quantity, but not for groundwater, and the groundwater protection requirements for soils shall be based on protection of the established point of exposure for groundwater as provided under this part; and

(3) The limitations provided under subparagraph (c)(3)(B) of Code Section 12-2-2 shall not apply to the director's decisions or actions under this part.

12-8-107.

At the participant's option, any or all of the following standards and policies may be considered and used in connection with the investigation and remediation of a voluntary remediation property under this part:

(1) SITE DELINEATION CONCENTRATION CRITERIA. Satisfactory evidence of the definition of the horizontal and vertical delineation of soil or groundwater contamination may be determined on the basis of any of the following concentrations:

(A) Upper limit concentrations from samples that are representative of local ambient or anthropogenic background conditions not affected by the subject site release;

(B) Soil concentrations less than those concentrations that require notification under standards promulgated by the board pursuant to Part 2 of this article;

(C) Two times the laboratory lower detection limit concentration using an applicable analytical test method recognized by the United States Environmental Protection Agency;

(D) For metals in soils, the upper limit concentration reported for Georgia undisturbed native soil background samples as reported in the United States Geological Survey (USGS) Open File Report 8 1-197 (Boerngen and Shacklette, 1981), or such later version as may be adopted by rule or regulation of the board; or

(E) Cleanup standards;

(2) EXPOSURE PATHWAY. An exposure pathway shall be considered complete if there are no discontinuities in or impediments to constituent of concern movement, including without limitation controls, from the source of the release to the receptor. Otherwise, the exposure pathway shall be incomplete and there shall be no exposure pathway that requires evaluation;

(3) REPRESENTATIVE EXPOSURE CONCENTRATIONS. Compliance with cleanup standards shall be determined on the basis of representative concentrations of constituents of concern in soils across each applicable soil exposure domain, and the representative concentrations for groundwater at a point of exposure established as the nearest of the following locations:

(A) Closest existing down gradient drinking water supply well;

(B) Likely nearest future location of a downgradient drinking water supply well where public supply water is not currently available and is not likely to be made available within the foreseeable future; and

(C) Hypothetical point of drinking water exposure located at a distance of 1000 feet downgradient from the delineated site contamination under this part;

(4) POINT OF DEMONSTRATION MONITORING FOR GROUNDWATER. Concentrations of site-specific constituents of concern in groundwater shall be measured and evaluated at a point of demonstration well to demonstrate that groundwater concentrations are protective of any established downgradient point of exposure;

(5) CLEANUP STANDARDS FOR SOIL. Compliance with cleanup standards for soil may be based on:

(A) Direct exposure factors for surficial soils within two feet of the land surface;

(B) Construction worker exposure factors for subsurface soils to a specified subsurface construction depth; and

(C) Soil concentrations for protection of groundwater criteria (at an established point of exposure for groundwater as defined under this part) for soils situated above the uppermost groundwater zone.

Whenever such depth-specific soil criteria are applied, the corrective action plan for the site shall include a description of the continuing actions and controls necessary to maintain compliance;

(6) CLEANUP STANDARD SELECTION FLEXIBILITY. A participant may select any cleanup standard without having to show or demonstrate that achieving other cleanup standards would not be feasible;

(7) FATE AND TRANSPORT PARAMETERS. Compliance with cleanup standards may be determined on the basis of any fate and transport model recognized by the United States Environmental Protection Agency or United States Geological Survey and using most probable representative values for model parameters, as adopted by the board;

(8) SOURCE MATERIAL. Compliance with cleanup standards that require that source material be removed may be satisfied when such material is removed, decontaminated, or stabilized to the extent practicable; and

(9) TECHNICAL IMPRACTICABILITY. Site delineation or remediation beyond the point of technical impracticability shall not be required if the site does not otherwise pose an imminent threat to human health and the environment."

SECTION 2.

All laws and parts of laws in conflict with this Act are repealed.