[Code of Federal Regulations]
[Title 40, Volume 22]
[Revised as of July 1, 2003]
From the U.S. Government Printing Office via GPO Access
[CITE: 40CFR257.27]

[Page 386-388]
 
                   TITLE 40--PROTECTION OF ENVIRONMENT
 
         CHAPTER I--ENVIRONMENTAL PROTECTION AGENCY (CONTINUED)
 
PART 257--CRITERIA FOR CLASSIFICATION OF SOLID WASTE DISPOSAL FACILITIES 
AND PRACTICES--Table of Contents
 
 Subpart B--Disposal Standards for the Receipt of Conditionally Exempt 
 Small Quantity Generator (CESQG) Wastes at Non-Municipal Non-Hazardous 
                          Waste Disposal Units
 
Sec. 257.27  Selection of remedy.

    (a) Based on the results of the corrective measures assessment 
conducted under Sec. 257.26, the owner or operator must select a remedy 
that, at a minimum, meets the standards listed in paragraph (b) of this 
section. The owner or operator must notify the State Director, within 14 
days of selecting a remedy, that a report describing the selected remedy 
has been placed in the operating record and how it meets the standards 
in paragraph (b) of this section.
    (b) Remedies must:
    (1) Be protective of human health and the environment;
    (2) Attain the ground-water protection standard as specified 
pursuant to Secs. 257.25 (h) or (i);
    (3) Control the source(s) of releases so as to reduce or eliminate, 
to the maximum extent practicable, further releases of appendix II 
(appendix II of 40 CFR part 258) constituents into the environment that 
may pose a threat to human health or the environment; and
    (4) Comply with standards for management of wastes as specified in 
Sec. 257.28(d).
    (c) In selecting a remedy that meets the standards of 
Sec. 257.27(b), the owner or operator shall consider the following 
evaluation factors:

[[Page 387]]

    (1) The long- and short-term effectiveness and protectiveness of the 
potential remedy(s), along with the degree of certainty that the remedy 
will prove successful based on consideration of the following:
    (i) Magnitude of reduction of existing risks;
    (ii) Magnitude of residual risks in terms of likelihood of further 
releases due to waste remaining following implementation of a remedy;
    (iii) The type and degree of long-term management required, 
including monitoring, operation, and maintenance;
    (iv) Short-term risks that might be posed to the community, workers, 
or the environment during implementation of such a remedy, including 
potential threats to human health and the environment associated with 
excavation, transportation, and re-disposal or containment;
    (v) Time until full protection is achieved;
    (vi) Potential for exposure of humans and environmental receptors to 
remaining wastes, considering the potential threat to human health and 
the environment associated with excavation, transportation, re-disposal, 
or containment;
    (vii) Long-term reliability of the engineering and institutional 
controls; and
    (viii) Potential need for replacement of the remedy.
    (2) The effectiveness of the remedy in controlling the source to 
reduce further releases based on consideration of the following factors:
    (i) The extent to which containment practices will reduce further 
releases;
    (ii) The extent to which treatment technologies may be used.
    (3) The ease or difficulty of implementing a potential remedy(s) 
based on consideration of the following types of factors:
    (i) Degree of difficulty associated with constructing the 
technology;
    (ii) Expected operational reliability of the technologies;
    (iii) Need to coordinate with and obtain necessary approvals and 
permits from other agencies;
    (iv) Availability of necessary equipment and specialists; and
    (v) Available capacity and location of needed treatment, storage, 
and disposal services.
    (4) Practicable capability of the owner or operator, including a 
consideration of the technical and economic capability.
    (5) The degree to which community concerns are addressed by a 
potential remedy(s).
    (d) The owner or operator shall specify as part of the selected 
remedy a schedule(s) for initiating and completing remedial activities. 
Such a schedule must require the initiation of remedial activities 
within a reasonable period of time taking into consideration the factors 
set forth in paragraphs (d)(1) through (d)(8) of this section. The owner 
or operator must consider the following factors in determining the 
schedule of remedial activities:
    (1) Extent and nature of contamination;
    (2) Practical capabilities of remedial technologies in achieving 
compliance with ground-water protection standards established under 
Secs. 257.25 (g) or (h) and other objectives of the remedy;
    (3) Availability of treatment or disposal capacity for wastes 
managed during implementation of the remedy;
    (4) Desirability of utilizing technologies that are not currently 
available, but which may offer significant advantages over already 
available technologies in terms of effectiveness, reliability, safety, 
or ability to achieve remedial objectives;
    (5) Potential risks to human health and the environment from 
exposure to contamination prior to completion of the remedy;
    (6) Resource value of the aquifer including:
    (i) Current and future uses;
    (ii) Proximity and withdrawal rate of users;
    (iii) Ground-water quantity and quality;
    (iv) The potential damage to wildlife, crops, vegetation, and 
physical structures caused by exposure to waste constituent;
    (v) The hydrogeologic characteristic of the unit and surrounding 
land;
    (vi) Ground-water removal and treatment costs; and

[[Page 388]]

    (vii) The cost and availability of alternative water supplies.
    (7) Practicable capability of the owner or operator.
    (8) Other relevant factors.
    (e) The Director of an approved State may determine that remediation 
of a release of an appendix II (appendix II of 40 CFR part 258) 
constituent from the unit is not necessary if the owner or operator 
demonstrates to the Director of the approved state that:
    (1) The ground-water is additionally contaminated by substances that 
have originated from a source other than the unit and those substances 
are present in concentrations such that cleanup of the release from the 
unit would provide no significant reduction in risk to actual or 
potential receptors; or
    (2) The constituent(s) is present in ground water that:
    (i) Is not currently or reasonably expected to be a source of 
drinking water; and
    (ii) Is not hydraulically connected with waters to which the 
hazardous constituents are migrating or are likely to migrate in a 
concentration(s) that would exceed the ground-water protection standards 
established under Sec. 257.25 (h) or (i); or
    (3) Remediation of the release(s) is technically impracticable; or
    (4) Remediation results in unacceptable cross-media impacts.
    (f) A determination by the Director of an approved State pursuant to 
paragraph (e) of this section shall not affect the authority of the 
State to require the owner or operator to undertake source control 
measures or other measures that may be necessary to eliminate or 
minimize further releases to the ground-water, to prevent exposure to 
the ground-water, or to remediate the ground-water to concentrations 
that are technically practicable and significantly reduce threats to 
human health or the environment.