[Comment: For dates of non-regulatory government publications,
publications of recognized organizations and associations, federal rules and
federal statutory provisions referenced in this rule, see rule
3745-1-03 of the Administrative
Code.]
(A) Requirements for
site-specific modifications to criteria and values. Criteria and values adopted
in, or developed pursuant to, this chapter may be modified on a site-specific
basis to reflect local environmental conditions
. These
criteria and values shall be developed and approved in accordance with
the following provisions
.
:
Any
(1)
Any such
modifications shall be
are protective of designated uses
and
, aquatic
life, wildlife, and human health and
be
are
submitted to the U.S. EPA for approval. Any
site-specific modifications shall be based on a sound scientific rationale. In
addition, any site-specific modifications that result in less stringent
criteria shall not be likely to jeopardize the continued existence of
threatened or endangered species or result in the destruction or adverse
modification of such species' critical habitat. More stringent modifications
shall be developed to protect threatened or endangered species, where such
modifications are necessary to ensure that water quality is not likely to
jeopardize the continued existence of such species or result in the destruction
or adverse modification of such species' critical habitat. More stringent
modifications may also be developed to protect candidate (C1) species being
considered by the United States fish and wildlife service for listing under
section 4 of the Endangered Species Act, where such modifications are necessary
to protect such species.
(2)
Any site-specific
modifications are based on a sound scientific rationale.
(3)
Any site-specific
modifications that result in less stringent criteria are not likely to
jeopardize the continued existence of threatened or endangered species or
result in the destruction or adverse modification of such species' critical
habitat. More stringent modifications are developed to protect threatened or
endangered species, where such modifications are necessary to ensure that water
quality is not likely to jeopardize the continued existence of such species or
result in the destruction or adverse modification of such species' critical
habitat. More stringent modifications may also be developed to protect
candidate (C1) species being considered by the United States fish and wildlife
service for listing under section 4 of the Endangered Species Act, where such
modifications are necessary to protect such species.
(B) Aquatic life.
(1) Aquatic life criteria or values may be
modified on a site-specific basis to provide an additional level of protection
where the toxicity or exposure potential is greater than the toxicity or
exposure potential assumptions used to derive the criteria or values in
question.
(2) Less stringent
site-specific modifications to chronic or acute aquatic life criteria or values
may be developed when either of the following occur:
(a) The local water quality characteristics
(such as, but not limited to, pH, hardness, temperature or color) lessen the
biological availability or toxicity of a pollutant.
(b) The sensitivity of the aquatic organisms
species that occur at the site differs from the species actually tested in
developing the criteria. The phrase "occur at the site" includes the species,
genera, families, orders, classes, and phyla that: are usually present at the
site; are present at the site only seasonally due to migration; are present
intermittently because they periodically return to or extend their ranges into
the site; were present at the site in the past and are not currently present at
the site due to degraded conditions but are expected to return to the site when
conditions improve; are present in nearby bodies of water and are not currently
present at the site due to degraded conditions but are expected to be present
at the site when conditions improve. The taxa that "occur at the site" cannot
be determined merely by sampling downstream and/or upstream of the site at one
point in time. "Occur at the site" does not include taxa that were once present
at the site but cannot exist at the site now due to permanent physical
alteration of the habitat at the site resulting, for example, from
dams.
(3) Less stringent
modifications also may be developed to acute and chronic aquatic life criteria
or values to reflect local physical and hydrological conditions.
(4) Less stringent modifications to the whole
effluent toxicity level for limited resource waters, as specified in rule
3745-2-09 of the Administrative
Code, may be applied. Documentation provided by the permittee or independently
available to the director shall show that the modification, not to exceed 1.0
acute toxic unit, is protective of the resident aquatic community.
(5) Any modifications to protect threatened
or endangered aquatic species
required by
specified in paragraph (A) of this rule may be
accomplished using either of the two following procedures:
(a) If the species mean acute value (SMAV)
for a listed or proposed species, or for a surrogate of such species, is lower
than the calculated final acute value (FAV), such lower SMAV may be used
instead of the calculated FAV in developing site-specific modified
criteria.
(b) The site-specific
criteria may be calculated using the recalculation procedure for site-specific
modifications described in chapter 3 of the "U.S. EPA Water Quality Standards
Handbook."
(C) Wildlife.
(1) Wildlife water quality criteria may be
modified on a site-specific basis to provide an additional level of protection
where the toxicity or exposure potential is greater than the toxicity or
exposure potential assumptions used to derive the criteria in
question.
(2) Less stringent
site-specific modifications to wildlife water quality criteria may be developed
provided all the following criteria apply:
(a)
The modification demonstration addresses both the mobility of prey organisms
and wildlife populations in defining the site for which the modification is
developed.
(b) The modification
reflects a site-specific bioaccumulation factor.
(c) There is a showing that both:
(i) Any increased uptake of the toxicant by
prey species utilizing the site will not cause adverse effects in wildlife
populations.
(ii) Wildlife
populations utilizing the site or downstream waters will continue to be fully
protected.
(3) Any modification to protect threatened or
endangered wildlife species
required by
specified in paragraph (A) of this rule must
consider both the mobility of prey organisms and wildlife populations in
defining the site for which criteria are developed, and may be accomplished by
using the following recommended method:
(a)
Use the methodology contained in rule
3745-1-43 of the Administrative
Code, substituting appropriate species-specific toxicological, epidemiological,
or exposure information, including changes to the BAF.
(b) Use an interspecies uncertainty factor of
one where epidemiological data are available for the species in question. If
necessary, species-specific exposure parameters can be derived in accordance
with rule
3745-1-43 of the Administrative
Code.
(c) Apply an intraspecies
uncertainty factor (to account for protection of individuals within a wildlife
population) in the denominator of the effect part of the wildlife equation
contained in rule
3745-1-43 of the Administrative
Code in a manner consistent with the other uncertainty factors described in
rule
3745-1-43 of the Administrative
Code.
(d) Compare the resulting
wildlife value for the species in question to the two class-specific wildlife
values which were previously calculated, then select the lowest of the three as
the site-specific modification.
(D) Bioaccumulation factors.
(1) BAFs may be modified on a site-specific
basis, pursuant to the methodology contained in rule
3745-1-41 of the Administrative
Code, to larger values where reliable data show that local bioaccumulation is
greater than the basin-wide value.
(2) BAFs may be modified on a site-specific
basis, pursuant to the methodology contained in rule
3745-1-41 of the Administrative
Code, to lower values if any of the following occur:
(a) The fraction of the total chemical that
is freely dissolved in the ambient water is different than that used to derive
the system-wide BAFs (i.e., the concentrations of particulate organic carbon
and the dissolved organic carbon are different than those used to derive the
system-wide BAFs).
(b) Input
parameters of the Gobas model, such as the structure of the aquatic food web
and the disequilibrium constant, are different at the site than those used to
derive the system-wide BAFs.
(c)
The per cent lipid of aquatic organisms that are consumed and occur at the site
is different than that used to derive the system-wide BAFs.
(d) Site-specific field-measured BAFs or
biota-sediment accumulation factor (BSAFs) are determined.
(3) Any more stringent modifications to
protect threatened or endangered species
required
by
specified in paragraph (A) of this
rule shall be derived using procedures set forth in the methodology contained
in rule
3745-1-41 of the Administrative
Code.
(E) Human health.
(1) Human health criteria or values may be
modified on a site-specific basis to provide an additional level of protection
where the toxicity or exposure potential is greater than the toxicity or
exposure potential assumptions used to derive the criteria or values in
question. Human health criteria or values shall be modified on a site-specific
basis to provide additional protection appropriate for highly exposed
subpopulations.
(2) Less stringent
site-specific modifications to human health criteria or values may be developed
when either of the following occur:
(a) Local
fish consumption rates are lower than the rate used to derive human health
criteria or values under rule
3745-1-42 of the Administrative
Code (this option
shall
is not be available for water bodies subject to a
fish consumption advisory).
(b) A
site-specific BAF is derived which is lower than that used to derive human
health criteria or values under rule
3745-1-42 of the Administrative
Code.
(F)
Notification requirements. When the director proposes a site-specific
modification to a criterion or value as allowed or required
specified in
paragraph (A) of this rule, the director shall notify the other Great Lakes
states of such a proposal and, for less stringent criteria,
supply
supplies appropriate justification.
(G) Notwithstanding paragraphs (A) to (F) of
this rule, any chemical-specific criterion listed in this chapter or derived
pursuant to rule 3745-1-40, 3745-1-41,
3745-1-42 or
3745-1-43 of the Administrative
Code may be modified for a particular surface water body or segment if specific
information is provided to the director which shows either of the following:
(1) That all, or portions, of the data used
to derive the criterion are inapplicable or not relevant to that surface water
body or segment.
(2) That the
otherwise applicable criterion is more or less stringent than necessary to
protect human health, aquatic life, wildlife or agricultural use.
In such cases, the director may adopt a less or more stringent
site-specific criterion if it can be scientifically justified based on new
toxicological data or site-specific conditions of water quality, pollutant
bioavailability, resident species, or human exposure.
(H) Within the lake Erie drainage
basin, paragraph (G) of this rule applies only when it results in modifications
at least as protective as modifications resulting from paragraphs (A) to (F) of
this rule.
Notes
Ohio Admin. Code
3745-1-39
Effective:
3/20/2024
Five Year Review (FYR) Dates:
8/21/2023 and
03/06/2028
Promulgated
Under: 119.03
Statutory
Authority: 6111.041
Rule
Amplifies: 6111.041
Prior
Effective Dates: 02/14/1978, 04/04/1985, 08/19/1985, 04/30/1987, 05/01/1990,
04/26/1997, 10/31/1997, 07/31/1999, 12/30/2002, 08/10/2016,
02/06/2017