Bill Text: GA HB248 | 2009-2010 | Regular Session | Comm Sub
NOTE: There are more recent revisions of this legislation. Read Latest Draft
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-Comm_Sub.html
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-Comm_Sub.html
09 LC 14
0075S
House
Bill 248 (COMMITTEE SUBSTITUTE)
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
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 provide an effective date; 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, to protect current
and likely future use of groundwater, 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, treatment
fixation, slurry walls, and vapor control systems. Engineered property
development features shall be acceptable as engineering controls provided these
features physically control or eliminate the potential for exposure to
contaminants of concern or control migration.
(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 of the following locations:
(A)
The closest existing down gradient drinking water supply well;
(B)
The 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; or
(C)
The hypothetical point of drinking water exposure located at a distance of 1000
feet downgradient from the delineated site contamination under this
part.
(12)
'Proof of financial assurance' means a mechanism, in a form specified by the
director, designed to demonstrate that sufficient funds will be available to
implement and maintain specific actions or controls. Mechanisms for proof of
financial assurance include, but are not limited to, insurance, trust funds,
surety bonds, letters of credit, performance bonds, certificates of deposit,
financial tests, and corporate guarantees.
(13)
'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.
(14)
'Representative concentration' means the average concentration to which a
specified receptor is exposed over an exposure duration within a relevant
exposure domain for soils or at an established or estimated point of exposure
for groundwater and consistent with United States Environmental Protection
Agency guidance for determination of average exposure
concentration.
(15)
'Voluntary remediation program' means the program established under this
part.
(16)
'Voluntary remediation property' means a qualifying property enrolled in the
voluntary remediation program.
(17)
'Technical impracticability' means the inability to fully delineate or remediate
contamination without incremental expenditures 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, voluntary
remediation 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; and
(6)
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 not:
(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.;
(B)
Be currently undergoing response activities required by an order of the regional
administrator of the federal Environmental Protection Agency; or
(C)
Be a facility required to have a permit under Code Section 12-8-66;
(3)
Qualifying the property under this part would not violate the terms and
conditions under which the division operates and administers remedial programs
by delegation or similar authorization from the United States Environmental
Protection Agency; and
(4)
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
participant in the voluntary remediation program must meet the following
criteria:
(1)
Be the property owner of the voluntary remediation property or have express
permission to enter another's property to perform corrective action including,
to the extent applicable, implementing controls for the site pursuant to written
lease, license, order, or indenture;
(2)
Not be in violation of any order, judgement, statute, rule, or regulation
subject to the enforcement authority of the director; and
(3)
Meet other such criteria as may be established by the board pursuant to Code
Section 12-8-103.
12-8-107.
(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 voluntary
remediation 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 experience in responsible charge of the investigation
and remediation of such releases. The voluntary remediation 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 voluntary
remediation plan shall be considered an application for enrollment in the
voluntary remediation program, and a nonrefundable application fee of $5,000.00
shall be submitted with the application. The director may, at any time, invoice
the participant for any costs to the division in reviewing the application or
subsequent document that exceed the initial application review fee, including
reasonably detailed itemization and justification of the costs. Failure to
remit payment within 60 days of receipt of such invoice may cause rejection of
the participant from the voluntary remediation program. The director may not
issue a written concurrence with a certification of compliance if there is an
outstanding fee to be paid by the participant.
(b)
Upon the director's approval of the voluntary remediation 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 at least 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 voluntary remediation 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 director may issue an order requiring the participant to submit proof of
financial assurance for continuing actions or controls upon issuance of the
director's approval with the voluntary remediation plan.
(d)
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 (e) 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 to implement the voluntary remediation 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 or
substantial danger to human health and the environment.
(e)
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.
(f)
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. The participant shall comply with the applicable public participation
requirements for compliance status reports as promulgated pursuant to Part 2 of
this article. 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.
(g)
In addition to other provisions of this part:
(1)
The director shall remove the voluntary remediation property from the inventory
if the participant demonstrates to the director at the time of enrollment, in
accordance with rules and regulations promulgated by the board pursuant to Part
2 of this article, that a release exceeding a reportable quantity did not exist
at the voluntary remediation property, unless the director issues a decision
that such release poses an imminent or substantial danger 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
for soil but was not listed on the inventory as a result of a release to
groundwater exceeding a reportable quantity, and if the participant further
demonstrates to the director at the time of enrollment that a release exceeding
a reportable quantity for groundwater does not exist at the voluntary
remediation property; 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. The director may require annual
groundwater monitoring for up to five years for a voluntary remeditation
property removed from the inventory pursuant to this paragraph unless the
director determines that further monitoring is necessary to protect human health
and the environment; 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.
(h)
Any voluntary remediation property or site relying on controls, including, but
not limited to, groundwater use restrictions for the purposes of certifying
compliance with cleanup standards, shall execute a covenant restricting such use
in conformance with O.C.G.A. 44-16-1, et seq., the 'Georgia Uniform
Environmental Covenants Act.' The division shall maintain an inventory of such
properties as provided for in that statute.
12-8-108.
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 for the purposes of this part
may be determined on the basis of any of the following concentrations; provided,
however, that the provisions of subparagraphs (B) and (C) of this paragraph
shall not be used if the concentrations are higher than as provided in
subparagraph (E) of this paragraph:
(A)
Concentrations from an appropriate number of 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, provided that such concentrations do not exceed all cleanup
standards;
(D)
For metals in soils, the concentrations reported for Georgia undisturbed native
soil 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)
Default, residential cleanup standards;
(2)
EXPOSURE
PATHWAY. A
site-specific 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 site-specific 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;
(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 site-specific 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 voluntary remediation plan
for the site shall include a description of the continuing actions and controls
necessary to maintain compliance;
(6)
AVAILABLE
CLEANUP
STANDARDS.
Any cleanup standard lawfully promulgated pursuant to Code Section 12-8-93 that
is protective of human health and the environment and accomplishes the
provisions, purposes, standards, and policies of this part may be used without
demonstrating that a different cleanup standard is inappropriate or
impracticable;
(7)
FATE
AND TRANSPORT
PARAMETERS.
Compliance with site-specific 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 site-specific cleanup standards that require that source
material be removed may be satisfied when such material is removed,
decontaminated, or otherwise immobilized in the subsurface, 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 or
substantial danger to human health and the
environment."
SECTION
2.
This
Act shall become effective on the first day of the month following the month in
which it is approved by the Governor or in which it becomes law without such
approval.
SECTION
3.
All
laws and parts of laws in conflict with this Act are repealed.