Guidelines Establishing Test Procedures for the Analysis of Pollutants; Analytical Methods for Biological Pollutants in Wastewater and Sewage Sludge: Final Rule, 14220-14233 [07-1455]
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Federal Register / Vol. 72, No. 57 / Monday, March 26, 2007 / Rules and Regulations
this final rule is promulgated as of 1
p.m. (Eastern time) on April 9, 2007 as
provided at 40 CFR 23.2 and 23.7.
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 136 and 503
EPA has established a
docket for this action under Docket ID
No. EPA–OW–2004–0014. All
documents in the docket are listed on
the www.regulations.gov Web site.
Although listed in the index, some
information is not publicly available,
e.g., CBI or other information whose
disclosure is restricted by statute.
Certain other material, such as
copyrighted material, is not placed on
the Internet and will be publicly
available only in hard copy form.
Publicly available docket materials are
available either electronically through
www.regulations.gov or in hard copy at
the HQ Water Docket Center, EPA/DC,
EPA West, Room B102, 1301
Constitution Ave., NW., Washington,
DC. The Public Reading Room is open
from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal
holidays. The telephone number for the
Public Reading Room is (202) 566–1744,
and the telephone number is (202) 566–
2426.
ADDRESSES:
[EPA–HQ–OW–2004–0014; FRL–8228–1]
RIN 2040–AE68
Guidelines Establishing Test
Procedures for the Analysis of
Pollutants; Analytical Methods for
Biological Pollutants in Wastewater
and Sewage Sludge: Final Rule
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: This rule modifies the EPA’s
Guidelines that establish approved
bacterial testing procedures for analysis
and sampling under the Clean Water
Act. EPA proposed these changes for
public comment on August 16, 2005 and
April 10, 2006. These changes include
approval for new methods for
monitoring microbial pollutants in
wastewater and sewage sludge,
including EPA methods, vendordeveloped methods and methods
developed by voluntary consensus
bodies (VCSB) as well as updated
versions of currently approved methods.
The addition of new and updated
methods to the wastewater regulations
provides increased flexibility to the
regulated community and laboratories
in the selection of analytical methods.
In addition, EPA has made a technical,
non-substantive correction.
DATES: This regulation is effective April
25, 2007. The incorporation by reference
of these methods is approved by the
Director of the Federal Register on April
25, 2007. For judicial review purposes,
Note: The EPA Docket Center suffered
damage due to flooding during the last week
of June 2006. The Docket Center is
continuing to operate. However, during the
cleanup, there will be temporary changes to
Docket Center telephone numbers, addresses,
and hours of operation for people who wish
to visit the Public Reading Room to view
documents. Consult EPA’s Federal Register
notice at 71 FR 38147 (July 5, 2006) or the
EPA website at https://www.epa.gov/
epahome/dockets.htm for current
information on docket status, locations and
telephone numbers.
For
information regarding the changes to
wastewater regulations, contact Robin
K. Oshiro, Engineering and Analysis
Division (4303T), USEPA Office of
Science and Technology, 1200
Pennsylvania Ave., NW., Washington,
DC 20460, 202–566–1075 (e-mail:
oshiro.robin@epa.gov).
FOR FURTHER INFORMATION CONTACT:
SUPPLEMENTARY INFORMATION:
A. Potentially Regulated Entities
1. Clean Water Act
EPA Regions, as well as States,
Territories and Tribes authorized to
implement the National Pollutant
Discharge Elimination System (NPDES)
program, issue permits with conditions
designed to ensure compliance with the
technology-based and water qualitybased requirements of the Clean Water
Act (CWA). These permits may include
restrictions on the quantity of pollutants
that may be discharged as well as
pollutant measurement and reporting
requirements. If EPA has approved test
procedures for analysis of a specific
pollutant, an NPDES permittee (or
applicant for an NPDES permit) must
use an approved test procedure (or an
approved alternate test procedure) for
the specific pollutant when testing for
the required waste constituent.
Similarly, if EPA has established permit
monitoring requirements, measurements
taken and reported under an NPDES
permit must comply with these
requirements. Therefore, entities with
NPDES permits will potentially be
regulated by the actions in this
rulemaking. Categories and entities that
may potentially be subject to the
requirements of today’s rule include:
Category
Examples of potentially regulated entities
State, Territorial, and Indian Tribal Governments ....................
States, Territories, and Tribes authorized to administer the NPDES permitting
program; States, Territories, and Tribes providing certification under Clean
Water Act section 401.
Facilities that must conduct monitoring to comply with NPDES permits.
POTWs that must conduct monitoring to comply with NPDES permits.
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Industry .....................................................................................
Municipalities ............................................................................
This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
regulated by this action. This table lists
types of entities that EPA is now aware
could potentially be regulated by this
action. Other types of entities not listed
in the table could also be regulated. To
determine whether your facility is
regulated by this action, you should
carefully examine the applicability
language at 40 CFR 122.1 (NPDES
purpose and scope), 40 CFR 136.1
(NPDES permits and CWA), 40 CFR
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403.1 (Pretreatment standards purpose
and applicability). If you have questions
regarding the applicability of this action
to a particular entity, consult the
appropriate person listed in the
preceding FOR FURTHER INFORMATION
CONTACT section.
What process governs judicial review of
this rule?
Under Section 509(b)(1) of the Clean
Water Act (CWA), judicial review of
today’s CWA rule may be obtained by
filing a petition for review in the United
States Circuit Court of Appeals within
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120 days from the date of promulgation
of this rule. For judicial review
purposes, this final rule is promulgated
as of 1 p.m. (Eastern time) on April 25,
2007 as provided at 40 CFR 23.2. The
requirements of this regulation may also
not be challenged later in civil or
criminal proceedings brought by EPA.
Abbreviations and Acronyms Used in
the Preamble and Final Rule
AOAC: Association of Official Analytical
Chemists International
ASTM: American Society for Testing and
Materials International
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CWA: Clean Water Act
EPA: Environmental Protection Agency
VCSB: Voluntary Consensus Standard Body
Table of Contents
I. Statutory Authority
Clean Water Act
II. Summary of Final Rule
A. 40 CFR Part 136
B. 40 CFR Part 503
III. Changes Between the Proposed Rule and
the Final Rule
A. Revision to 40 CFR Part 136,
Applicability
B. Revision to 40 CFR Part 136,
Identification of Test Procedures
C. Revision to 40 CFR Part 136, Table IA
Title
D. Revisions to 40 CFR Part 136, Table II
and Footnotes
E. Revisions to 40 CFR Part 503, Sampling
and Analysis
IV. Response to Comments
Lack of Connecting Language Between 40
CFR Parts 136 and 503 for Sewage
Sludge Methods
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory
Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation
and Coordination with Indian Tribal
Governments
G. Executive Order 13045: Protection of
Children from Environmental Health
Risks and Safety Risks
H. Executive Order 13211: Actions that
Significantly Affect Energy Supply,
Distribution, or Use
I. National Technology Transfer and
Advancement Act
J. Congressional Review Act
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I. Statutory Authority
Clean Water Act
EPA is promulgating today’s rule
pursuant to the authority of sections
301(a), 304(h), and 501(a) of the Clean
Water Act (‘‘CWA’’ or the ‘‘Act’’), 33
U.S.C. 1311(a), 1314(h), 1361(a). Section
301(a) of the Act prohibits the discharge
of any pollutant into navigable waters
unless the discharge complies with a
National Pollutant Discharge
Elimination System (NPDES) permit
issued under section 402 of the Act.
Section 304(h) of the Act requires the
Administrator of the EPA to ‘‘* * *
promulgate guidelines establishing test
procedures for the analysis of pollutants
that shall include the factors which
must be provided in any certification
pursuant to [section 401 of this Act] or
permit application pursuant to [section
402 of this Act].’’ Section 501(a) of the
Act authorizes the Administrator to
‘‘* * * prescribe such regulations as are
necessary to carry out this function
under [the Act].’’ EPA generally has
codified its test procedure regulations
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(including analysis and sampling
requirements) for CWA programs at 40
CFR Part 136, though some
requirements are codified in other Parts
(e.g., 40 CFR Chapter I, Subchapters N
and O).
II. Summary of Final Rule
The following sections describe the
changes EPA is making in today’s final
rule.
A. 40 CFR Part 136
This rule approves new and revised
methods for inclusion in 40 CFR Part
136. These methods include EPA
methods, vendor methods submitted by
IDEXX and Hach, and voluntary
consensus standards.
The following discussion briefly
describes the changes to Part 136
methods approved today.
1. This rule amends the regulations at
40 CFR Part 136 to approve five E. coli
and two enterococci methods for
monitoring microbial pollutants in
wastewaters. The E. coli methods
include EPA Method 1603 (modified
mTEC), and vendor methods Colilert
and Colilert-18, and mColiBlue24.
The enterococci methods include EPA
Method 1600 (mEI), and vendor method
EnterolertTM.
2. The rule approves two fecal
coliform and one Salmonella method for
monitoring microbial pollutants in
sewage sludge (biosolids). The fecal
coliform methods include EPA Methods
1680 (LT–EC) and 1681 (A–1) and the
Salmonella Method 1682 (Modified
MSRV). The methods approved today
are alternative methods to those
currently prescribed for measuring fecal
coliform and salmonella in sewage
sludge identified in 40 CFR § 503.8(b).
3. The rule amends the regulations by
moving the microbial methods approved
for use in ambient waters from Table IA
to a new Table IH, and adding Table IH
to section 136.3(a).
4. The rule extends the holding time
for fecal coliforms using EPA Methods
1680 (LTB–EC) or 1681 (A–1) in sewage
sludge for Class A composted, Class B
aerobically or anaerobically digested
sewage sludge.
5. The rule amends 40 CFR 136.1 to
add a new provision that authorizes the
use of the methods identified at 40 CFR
503.8(b) and the newly approved Part
136 methods for fecal coliform and
Salmonella for permit applications and
recordkeeping and reporting required
under EPA’s sewage sludge regulations
at 40 CFR Part 503.
B. 40 CFR Part 503
This rule amends the regulations at 40
CFR Part 503 by adding a cross
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reference to the 40 CFR Part 136
methods in section 503.8(b).
III. Changes Between the Proposed Rule
and the Final Rule
Except as noted below, the content of
the final rule is the same as that of the
proposed rule. In some instances, EPA
revised for clarity the language of the
final rule from that in the proposed rule.
A. Revision to 40 CFR Part 136,
Applicability
Based on comment received on the
Agency’s proposal of methods for use in
sewage sludge, EPA has amended the
applicability provision to clarify that the
applicable procedures of Part 136 and
Part 503 must be used for measurements
for sewage sludge permit applications
and reporting and recordkeeping
requirements under Part 503.
B. Revision to 40 CFR Part 136,
Identification of Test Procedures
Section 553 of the Administrative
Procedure Act, 5 U.S.C. 553(b)(B),
provides that, when an agency for good
cause finds that notice and public
procedure are impracticable,
unnecessary or contrary to the public
interest, the agency may issue a rule
without providing notice and an
opportunity for public comment. EPA
has determined that there is good cause
for making today’s changes to the rule
final without prior proposal and
opportunity for comment. Notice and
opportunity for public comment is not
necessary with respect to these changes
because they are not substantive and
merely correct errors in cross-referenced
provisions as explained below.
Section 136.3(a) provides that
discharge parameter values for which
reports are required must be determined
either by the standard analytical test
procedures described in the tables in
Part 136 or approved additional or
alternate test procedures. EPA has
modified the language of 40 CFR
136.3(a) to make three corrections. First,
EPA has changed the citation in the last
sentence before Table IA from
‘‘paragraphs (b) or (c) of this section or
40 CFR 401.13’’ to ‘‘paragraphs (c) of
this section, 40 CFR 136.5(a)–(d) and 40
CFR 401.13.’’ Paragraph (b) does not
describe circumstances in which
alternate procedures may be approved
while section 136.5 does.
Second, EPA has deleted the clause at
the end of the last sentence which states
that other test procedures may be used
‘‘* * * when such other test procedures
have been previously approved by the
Regional Administrator of the Region in
which the discharge will occur, and
providing the Director of the State in which
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the discharge will occur does not object to
the use of such alternate test procedure
* * *.’’
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Only two of the cited provisions require
approval by the Regional Administrator
or Director of a State. 40 CFR 401.13
does not because it pertains to variances
of guidelines of national applicability.
The cross-referenced provisions
authorize the use of additional or
alternate test procedures in described
circumstances. Thus, section 136.3(c)
authorizes approval by the Regional
Administrator (or Director of an
approved State NPDES Program) for
analysis of additional pollutants or
parameters required to be reported for a
particular discharge. Section 136.5(a)–
(d) authorizes approval by the Regional
Administrator of alternate procedures
for use within a particular EPA Region.
40 CFR section 401.13 authorizes the
use of analytical procedures that are
specifically defined in 40 CFR Parts
402–699. This last category of analytical
procedures that are promulgated for
specific effluent limitations guidelines
and pretreatment standards and not
codified in Part 136 do not require the
approval of the Director of a State as the
current language erroneously implies.
Third, EPA removed an erroneous
reference that was listed as a source for
the methods listed in section 136.3.
EPA has modified the regulation to
provide the correct citation and delete
the inaccurate and misleading language.
None of the changes EPA is
promulgating today are themselves
substantive but rather, as noted, only
either correct an error in citing to the
other applicable provisions of these
regulations or correct inaccuracies. The
substantive provisions in question were
previously subject to notice and
comment. Thus, notice and public
procedures are unnecessary. EPA finds
that this constitutes good cause under 5
U.S.C. 553(b)(B).
C. Revision to 40 CFR Part 136, Table
IA Title
The rule revises the title to Table IA
from ‘‘List of Approved Biological
Methods’’ to ‘‘List of Approved
Biological Methods for Wastewater and
Sewage Sludge.’’ Today’s action
updating Table IA at § 136.3 more
clearly defines the removal of approved
microbiological methods for ambient
waters from this table. Such methods
have been moved to a new table, Table
IH.
D. Revisions to 40 CFR Part 136, Table
II and Footnotes
The rule revises Table II (Required
Containers, Preservation Techniques,
and Holding Times), and the footnotes
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to Table II at 40 CFR 136.3(e). Today’s
action updating Table II at § 136.3(e)
more clearly defines the holding time
for bacterial testing as 6 hours holding
time with 2 hours to process samples.
E. Revision to 40 CFR Part 503,
Sampling and Analysis
Based on comments received on the
Agency’s proposal of methods for use in
sewage sludge, EPA is including a cross
reference to 40 CFR Part 136 in 40 CFR
503.8(b) which prescribes the methods
that must be used for sampling and
analysis of sewage sludge.
IV. Response to Comments
EPA received 39 comments regarding
methods included in this final rule from
the August 16, 2005 proposal (70 FR
48256), and 9 comments on the April
10, 2006 Notice of Data Availability
(NODA) (71 FR 18329). Commentors
represented a number of different
interests, including analytical
laboratories, water utilities, instrument
manufacturers, State and local
governments, trade associations,
scientists, and private citizens. The
public docket for this rule includes the
Agency’s response to all comments. The
majority of the comments were with
regard to method inclusion, method use,
and quality control requirements. The
following is a summary of our response
to comments about the lack of
connecting language between 40 CFR
Parts 136 and 503 for sewage sludge
methods.
EPA proposed to approve methods in
40 CFR Part 136 for sewage sludge but
did not include an appropriate cross
reference in 40 CFR Part 503 to Part 136
so as to allow the use of appropriate 40
CFR 136.3 methods as alternative
methods to those listed in 40 CFR 503.8.
Based on comments to the proposal,
EPA has amended the language in 40
CFR 503.8(b). In addition, as discussed
above, EPA has also amended the
language in 40 CFR 136.1 regarding the
applicability of the methods in this
section to 40 CFR Part 503.
V. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
This action is not a ‘‘significant
regulatory action’’ under the terms of
Executive Order (EO) 12866 (58 FR
51735, October 4, 1993) and is therefore
not subject to review under the EO.
B. Paperwork Reduction Act
This action does not impose an
information collection burden under the
provisions of the Paperwork Reduction
Act, 44 U.S.C. 3501 et seq. This rule
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does not impose any information
collection, reporting, or recordkeeping
requirements. This rule merely adds
new and updated versions of testing
procedures, withdraws some older
testing procedures, and establishes new
sample collection, preservation, and
holding time requirements.
Burden means the total time, effort, or
financial resources expended by persons
to generate, maintain, retain, or disclose
or provide information to or for a
Federal agency. This includes the time
needed to review instructions; develop,
acquire, install, and utilize technology
and systems for the purpose of
collecting, validating, and verifying
information, processing and
maintaining information, and disclosing
and providing information; adjust the
existing ways to comply with any
previously applicable instructions and
requirements; train personnel to be able
to respond to a collection of
information; search data sources;
complete and review the collection of
information; and transmit or otherwise
disclose the information.
An Agency may not conduct or
sponsor, and a person is not required to
respond to a collection of information
unless it displays a currently valid OMB
control number. The OMB control
numbers for EPA’s regulations in 40
CFR are listed in 40 CFR Part 9.
C. Regulatory Flexibility Act
The RFA generally requires an agency
to prepare a regulatory flexibility
analysis of any rule subject to notice
and comment rulemaking requirements
under the Administrative Procedure Act
or any other statute unless the agency
certifies that the rule will not have a
significant economic impact on a
substantial number of small entities.
Small entities include small businesses,
small organizations, and small
governmental jurisdictions.
For purposes of assessing the impacts
of this rule on small entities for methods
under the Clean Water Act, small entity
is defined as: (1) A small business as
defined by the Small Business
Administration’s (SBA) regulations at 13
CFR 121.201; (2) a small governmental
jurisdiction that is a government of a
city, county, town, school district or
special district with a population less
than 50,000; and (3) a small
organization that is any not-for-profit
enterprise which is independently
owned and operated and is not
dominant in its field.
After considering the economic
impacts of today’s final rule on small
entities, I certify that this action will not
have a significant economic impact on
a substantial number of small entities.
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This final rule will not impose any
requirements on small entities. This
action approves new and updated
versions of testing procedures,
withdraws some older testing
procedures, and approves new sample
collection, preservation, and holding
time requirements. Generally, these
changes will have a positive impact on
small entities by increasing method
flexibility, thereby allowing entities to
reduce costs by choosing more costeffective methods. In some cases,
analytical costs may increase slightly
due to the additional QC requirements
included in the methods that are being
approved. However, most laboratories
that analyze samples for EPA
compliance monitoring have already
instituted QC requirements as part of
their laboratory practices.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates
Reform Act of 1995 (UMRA), Public
Law 104–4, establishes requirements for
Federal agencies to assess the effects of
their regulatory actions on State, Tribal,
and local governments and the private
sector. Under section 202 of the UMRA,
EPA generally must prepare a written
statement, including a cost-benefit
analysis, for proposed and final rules
with ‘‘Federal mandates’’ that may
result in expenditures to State, local,
and Tribal governments, in the
aggregate, or to the private sector, of
$100 million or more in any one year.
Before promulgating an EPA rule for
which a written statement is needed,
section 205 of the UMRA generally
requires EPA to identify and consider a
reasonable number of regulatory
alternatives and adopt the least costly,
most cost-effective or least burdensome
alternative that achieves the objectives
of the rule. The provisions of section
205 do not apply when they are
inconsistent with applicable law.
Moreover, section 205 allows EPA to
adopt an alternative other than the least
costly, most cost-effective or least
burdensome alternative if the
Administrator publishes with the final
rule an explanation of why that
alternative was not adopted.
Before EPA establishes any regulatory
requirements that may significantly or
uniquely affect small governments,
including Tribal governments, it must
have developed under section 203 of the
UMRA a small government agency plan.
The plan must provide for the
notification of potentially affected small
governments, enabling officials of
affected small governments to have
meaningful and timely input in the
development of EPA regulatory
proposals with significant Federal
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intergovernmental mandates, and
informing, educating, and advising
small governments on compliance with
the regulatory requirements.
This rule contains no Federal
mandates (under the regulatory
provisions of Title II of UMRA) for
State, local, or Tribal governments or
the private sector. The rule imposes no
enforceable duty on any State, local, or
Tribal governments or the private sector.
In fact, this rule should (on the whole)
save money for governments and the
private sector by increasing method
flexibility, and allowing these entities to
reduce monitoring costs by taking
advantage of innovations. Thus, today’s
rule is not subject to the requirements
of Sections 202 and 205 of the UMRA.
EPA has determined that this rule
contains no regulatory requirements that
might significantly or uniquely affect
small governments. Generally, this
action will have a positive impact by
increasing method flexibility, thereby
allowing method users to reduce costs
by choosing more cost effective
methods. In some cases, analytical costs
may increase slightly due to changes in
methods, but these increases are neither
significant nor unique to small
governments. This rule merely approves
new and updated versions of testing
procedures, withdraws some older
testing procedures, and approves new
sample collection, preservation, and
holding time requirements. Thus,
today’s rule is not subject to the
requirements of Section 203 of UMRA.
E. Executive Order 13132: Federalism
Executive Order 13132, entitled
‘‘Federalism’’ (64 FR 43255, August 10,
1999), requires EPA to develop an
accountable process to ensure
‘‘meaningful and timely input by State
and local officials in the development of
regulatory policies that have federalism
implications.’’ ‘‘Policies that have
federalism implications’’ is defined in
the Executive Order to include
regulations that have ‘‘substantial direct
effects on the States, on the relationship
between the national government and
the States, or on the distribution of
power and responsibilities among the
various levels of government.’’
This final rule does not have
federalism implications. It will not have
substantial direct effects on the States,
on the relationship between the national
government and the States, or on the
distribution of power and
responsibilities among the various
levels of government, as specified in
Executive Order 13132. This rule merely
approves new and updated versions of
testing procedures, withdraws some
older testing procedures, and approves
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new sample collection, preservation,
and holding time requirements. The
costs to State and local governments
will be minimal (in fact, governments
may see a cost savings), and the rule
does not preempt State law. Thus,
Executive Order 13132 does not apply
to this rule.
In the spirit of Executive Order 13132,
and consistent with EPA policy to
promote communications between EPA
and State and local governments, EPA
specifically solicited comment on the
proposed rule from State and local
officials.
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
Executive Order 13175, entitled
‘‘Consultation and Coordination with
Indian Tribal Governments’’ (65 FR
67249, November 9, 2000), requires EPA
to develop an accountable process to
ensure ‘‘meaningful and timely input by
tribal officials in the development of
regulatory policies that have tribal
implications.’’
This final rule does not have tribal
implications, as specified in Executive
Order 13175. It will not have substantial
direct effects on Tribal governments, on
the relationship between the Federal
government and Indian tribes, or on the
distribution of power and
responsibilities between the Federal
government and Indian tribes. This rule
merely approves new and updated
versions of testing procedures,
withdraws some older testing
procedures, and approves new sample
collection, preservation, and holding
time requirements. The costs to Tribal
governments will be minimal (in fact,
governments may see a cost savings),
and the rule does not preempt State law.
Thus, Executive Order 13175 does not
apply to this rule.
G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
Executive Order 13045: ‘‘Protection of
Children from Environmental Health
Risks and Safety Risks’’ (62 FR 19885,
April 23, 1997) applies to any rule that:
(1) Is determined to be ‘‘economically
significant’’ as defined under Executive
Order 12866, and (2) concerns an
environmental health or safety risk that
EPA has reason to believe may have a
disproportionate effect on children. If
the regulatory action meets both criteria,
the Agency must evaluate the
environmental health or safety effects of
the planned rule on children, and
explain why the planned regulation is
preferable to other potentially effective
and reasonably feasible alternatives
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from Association of Official Analytical
Chemists International, 481 North
Frederick Avenue, Suite 500,
Gaithersburg, MD 20877–2417, and
ASTM methods can be obtained from
ASTM International, 100 Barr Harbor
Drive, West Conshohocken, PA 19428.
These newly approved procedures
reflect improvements in science and
technology. EPA believes that the
addition of these methods offer a wider
variety of options that may be more cost
effective to conduct compliance
monitoring of bacterial pollutants.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
This rule is not subject to Executive
Order 13211, ‘‘Actions Concerning
Regulations That Significantly Affect
Energy Supply, Distribution, or Use’’ (66
FR 28355 (May 22, 2001)) because it is
not a significant regulatory action under
Executive Order 12866.
cprice-sewell on PROD1PC66 with RULES2
considered by the Agency. This final
rule is not subject to the Executive
Order 13045 because it is not
economically significant as defined in
Executive Order 12866. Further it does
not concern an environmental health or
safety risk that EPA has reason to
believe may have a disproportionate
effect on children. This action approves
new and updated versions of testing
procedures, withdraws some older
testing procedures, and approves new
sample collection, preservation, and
holding time requirements.
J. Congressional Review Act
I. National Technology Transfer and
Advancement Act
As noted in the proposed rule,
Section 12(d) of the National
Technology Transfer and Advancement
Act of 1995, (NTTAA), Public Law 104–
113, section 12(d) (15 U.S.C. 272 note),
directs EPA to use voluntary consensus
standards in its regulatory activities
unless to do so would be inconsistent
with applicable law or otherwise
impractical. Voluntary consensus
standards are technical standards (e.g.,
material specifications, test methods,
sampling procedures, and business
practices) that are developed or adopted
by voluntary consensus standard bodies.
The NTTAA directs EPA to provide
Congress, through the OMB,
explanations when the Agency decides
not to use available and applicable
voluntary consensus standards. This
rulemaking involves technical
standards. EPA has decided to use E.
coli, enterococci and fecal coliform
methods published in Standard
Methods and ASTM International.
The E. coli methods from Standard
Methods are method 9223B (Standard
Methods 18th, 19th and 20th Editions)
and method 9223 B–97 (Standard
Methods Online Edition), as well as
AOAC method 991.15. The enterococci
method from ASTM is method D6503–
99. The fecal coliform methods from
Standard Methods are methods 9221 C
E (Standard Methods 18th, 19th and
20th Editions) and method 9221 C E–99
(Standard Methods Online Edition).
Standard Methods can be obtained from
American Public Health Association,
1015 15th Street, NW., Washington DC
20005, AOAC methods can be obtained
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The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this rule and other
required information to the U.S. Senate,
the U.S. House of Representatives, and
the Comptroller General of the United
States prior to publication of the rule in
the Federal Register. A major rule
cannot take effect until 60 days after it
is published in the Federal Register.
This action is not a ‘‘major rule’’ as
defined by 5 U.S.C. 804(2). This rule
will be effective April 25, 2007.
List of Subjects
40 CFR Part 136
Environmental protection,
Incorporation by reference, Reporting
and recordkeeping requirements, Water
pollution control.
40 CFR Part 503
Environmental protection, Reporting
and recordkeeping requirements, Waste
treatment and disposal, Water pollution
control.
Dated: September 28, 2006.
Stephen L. Johnson,
Administrator.
For the reasons set out in the
preamble, title 40, chapter I of the Code
of Federal Regulations, is amended as
follows:
I
PART 136—GUIDELINES
ESTABLISHING TEST PROCEDURES
FOR THE ANALYSIS OF POLLUTANTS
1. The authority citation for Part 136
continues to read as follows:
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2. Section 136.1 is revised to read as
follows:
I
§ 136.1
Applicability.
(a) The procedures prescribed herein
shall, except as noted in § 136.5, be used
to perform the measurements indicated
whenever the waste constituent
specified is required to be measured for:
(1) An application submitted to the
Administrator, or to a State having an
approved NPDES program for a permit
under section 402 of the Clean Water
Act of 1977, as amended (CWA), and/or
to reports required to be submitted
under NPDES permits or other requests
for quantitative or qualitative effluent
data under parts 122 to 125 of title 40,
and,
(2) Reports required to be submitted
by dischargers under the NPDES
established by parts 124 and 125 of this
chapter, and,
(3) Certifications issued by States
pursuant to section 401 of the CWA, as
amended.
(b) The procedure prescribed herein
and in part 503 of title 40 shall be used
to perform the measurements required
for an application submitted to the
Administrator or to a State for a sewage
sludge permit under section 405(f) of
the Clean Water Act and for
recordkeeping and reporting
requirements under part 503 of title 40.
I 3. Section 136.3 is amended as
follows:
I a. By revising paragraph (a)
introductory text and Table IA.
I b. In paragraph (a) by adding Table IH
after the notes of Table IG.
I c. In paragraph (b) by revising the
introductory text and by revising
references 2, 6, 10, 11, 34, 38, 39, and
52 through 62; and by adding references
70 through 72.
I d. By revising paragraph (e).
§ 136.3
Editorial Note: The Office of the Federal
Register received this document on March 8,
2007.
I
Authority: Secs. 301, 304(h), 307, and
501(a) Pub. L. 95–217, 91 Stat. 1566, et seq.
(33 U.S.C. 1251, et seq.) (The Federal Water
Pollution Control Act Amendments of 1972
as amended by the Clean Water Act of 1977.)
Identification of test procedures.
(a) Parameters or pollutants, for which
methods are approved, are listed
together with test procedure
descriptions and references in Tables
IA, IB, IC, ID, IE, IF, IG, and IH. In the
event of a conflict between the reporting
requirements of 40 CFR Parts 122 and
125 and any reporting requirements
associated with the methods listed in
these tables, the provisions of 40 CFR
Parts 122 and 125 are controlling and
will determine a permittee’s reporting
requirements. The full text of the
referenced test procedures are
incorporated by reference into Tables
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IA, IB, IC, ID, IE, IF, IG, and IH. The
incorporation by reference of these
documents, as specified in paragraph (b)
of this section, was approved by the
Director of the Federal Register in
accordance with 5 U.S.C. 552(a) and 1
CFR Part 51. Copies of the documents
may be obtained from the sources listed
in paragraph (b) of this section.
Documents may be inspected at EPA’s
Water Docket, EPA West, 1301
Constitution Avenue, NW., Room B102,
Washington, DC (Telephone: 202–566–
2426); or at the National Archives and
Records Administration (NARA). For
information on the availability of this
material at NARA, call 202–741–6030,
or go to: https://www.archives.gov/
federal_register/
code_of_federal_regulations/
ibr_locations.html. These test
procedures are incorporated as they
exist on the day of approval and a notice
of any change in these test procedures
will be published in the Federal
Register. The discharge parameter
values for which reports are required
must be determined by one of the
standard analytical test procedures
incorporated by reference and described
in Tables IA, IB, IC, ID, IE, IF, IG, and
IH or by any alternate test procedure
which has been approved by the
Administrator under the provisions of
paragraph (d) of this section and
§§ 136.4 and 136.5. Under certain
circumstances paragraph (c) of this
section, § 136.5(a) through (d) or 40 CFR
401.13, other additional or alternate test
procedures may be used.
TABLE IA.—LIST OF APPROVED BIOLOGICAL METHODS FOR WASTEWATER AND SEWAGE SLUDGE
Standard methods 18th, 19th,
20th ed.
Standard methods online
AOAC, ASTM,
USGS
Parameter and units
Method 1
EPA
Bacteria:
1. Coliform (fecal),
number per 100
mL or number per
gram dry weight.
Most Probable Number
(MPN),5 tube 3 dilution, or
p. 132 3 ............
1680 12,14 .........
1681 12,19 .........
9221 C E .........
9221 C E–99.
Membrane filter (MF) 2,
single step.
MPN, 5 tube, 3 dilution,
or
p. 124 3 ............
9222 D ............
9222 D–97 .........
p. 132 3 ............
9221 C E .........
9221 C E–99.
MF 2, single step ..........
MPN, 5 tube, 3 dilution,
or
p. 124 3 ............
p. 114 3 ............
9222 D ............
9221 B .............
9222 D–97.
9221 B–99.
MF 2, single step or two
step.
MPN, 5 tube, 3 dilution,
or
p. 108 3 ............
9222 B .............
9222 B–97 .........
p. 114 3 ............
9221 B .............
9221 B–99.
MF 2 with enrichment ...
p. 111 3 ............
9222 (B+B.5c)
MPN 7,9,15 multiple
tube/multiple well.
.........................
9223 B 13 .........
9222
(B+B.5c)¥97.
9223 B–97 13 .....
991.15 11 .........
MF 2,6,7,8,9 single step ..
1603 21 ............
.........................
............................
.........................
MPN, 5 tube 3 dilution,
p. 139 3 ............
9230 B .............
9230 B–93.
MF 2, or ........................
Plate count ...................
MPN 7,9, multiple tube/
multiple well.
MF 2,6,7,8,9 single step ..
MPN multiple tube .......
p. 136 3 ............
p. 143 3.
.........................
9230 C ............
9230 C–93 .........
B–0055–85 5.
.........................
............................
D6503–99 10 ....
Ceriodaphnia dubia
acute.
2002.0 25.
Daphnia puplex and
Daphnia magna
acute.
Fathead Minnow,
Pimephales
promelas, and
Bannerfin shiner,
Cyprinella leedsi,
acute.
2021.0 25.
2. Coliform (fecal) in
presence of chlorine, number per
100 mL.
3. Coliform (total),
number per 100
mL.
4. Coliform (total), in
presence of chlorine, number per
100 mL.
5. E. coli, number
per 100 mL 20.
6. Fecal streptococci,
number per 100
mL.
7. Enterococci, number per 100 mL 20.
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8. Salmonella, number per gram dry
weight 12.
Aquatic Toxicity:
9. Toxicity, acute,
fresh water organisms, LC 50, percent effluent.
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B–0025–8 5.
1600 24.
1682 22.
2000.0 25.
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TABLE IA.—LIST OF APPROVED BIOLOGICAL METHODS FOR WASTEWATER AND SEWAGE SLUDGE—Continued
Method 1
Parameter and units
10. Toxicity, acute,
estuarine and marine organisms of
the Atlantic Ocean
and Gulf of Mexico, LC50, percent
effluent.
11. Toxicity, chronic,
fresh water organisms, NOEC or
IC25, percent effluent.
12. Toxicity, chronic,
estuarine and marine organisms of
the Atlantic Ocean
and Gulf of Mexico, NOEC or IC25,
percent effluent.
EPA
Rainbow Trout,
Oncorhynchus
mykiss, and brook
trout, Salvelinus
fontinalis, acute.
Mysid, Mysidopsis
bahia, acute.
Standard methods online
AOAC, ASTM,
USGS
2004.0 25.
Fathead minnow,
Pimephales
promelas, embryolarval survival and
teratogenicity.
Daphnia, Ceriodaphnia
dubia, survival and
reproduction.
Green alga,
Selenastrum
capricornutum,
growth.
Sheepshead minnow,
Cyprinodon
variegatus, larval survival and growth.
Sheepshed minnow,
Cyprinodon
variegatus, embryolarval survival and
teratogenicity.
Inland silverside,
Menidia beryllina, larval survival and
growth.
Mysid, Mysidopsis
bahia, survival,
growth, and fecundity.
Sea urchin, Arbacia
punctulata, fertilization.
2007.0 25.
2006.0 25.
1000.0 26.
1001.0 26.
1002.0 26.
1003.0 26.
1004.0 27.
1005.0 27.
1006.0 27.
1007.0 27.
1008.0 27.
1 The
method must be specified when results are reported.
0.45 µm membrane filter (MF) or other pore size certified by the manufacturer to fully retain organisms to be cultivated and to be free of
extractables which could interfere with their growth.
3 USEPA. 1978. Microbiological Methods for Monitoring the Environment, Water, and Wastes. Environmental Monitoring and Support Laboratory, U.S. Environmental Protection Agency, Cincinnati, OH, EPA/600/8–78/017.
4 [Reserved].
5 USGS. 1989. U.S. Geological Survey Techniques of Water-Resource Investigations, Book 5, Laboratory Analysis, Chapter A4, Methods for
Collection and Analysis of Aquatic Biological and Microbiological Samples, U.S. Geological Survey, U.S. Department of the Interior, Reston, VA.
6 Because the MF technique usually yields low and variable recovery from chlorinated wastewaters, the Most Probable Number method will be
required to resolve any controversies.
7 Tests must be conducted to provide organism enumeration (density). Select the appropriate configuration of tubes/filtrations and dilutions/volumes to account for the quality, character, consistency, and anticipated organism density of the water sample.
2A
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Other
2019.0 25.
Sheepshead Minnow,
Cyprinodon
variegatus, acute.
Silverside, Menidia
beryllina, Menidia
menidia, and Menidia
peninsulae, acute.
Fathead minnow,
Pimephales
promelas, larval survival and growth.
Standard methods 18th, 19th,
20th ed.
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8 When the MF method has been used previously to test waters with high turbidity, large numbers of noncoliform bacteria, or samples that may
contain organisms stressed by chlorine, a parallel test should be conducted with a multiple-tube technique to demonstrate applicability and comparability of results.
9 To assess the comparability of results obtained with individual methods, it is suggested that side-by-side tests be conducted across seasons
of the year with the water samples routinely tested in accordance with the most current Standard Methods for the Examination of Water and
Wastewater or EPA alternate test procedure (ATP) guidelines.
10 ASTM. 2000, 1999, 1996. Annual Book of ASTM Standards—Water and Environmental Technology. Section 11.02. ASTM International. 100
Barr Harbor Drive, West Conshohocken, PA 19428.
11 AOAC. 1995. Official Methods of Analysis of AOAC International, 16th Edition, Volume I, Chapter 17. Association of Official Analytical
Chemists International. 481 North Frederick Avenue, Suite 500, Gaithersburg, MD 20877–2417.
12 Recommended for enumeration of target organism in sewage sludge.
13 These tests are collectively known as defined enzyme substrate tests, where, for example, a substrate is used to detect the enzyme b-glucuronidase produced by E. coli.
14 USEPA. July 2006. Method 1680: Fecal Coliforms in Sewage Sludge (Biosolids) by Multiple-Tube Fermentation Using Lauryl-Tryptose Broth
(LTB) and EC Medium. US Environmental Protection Agency, Office of Water, Washington, DC EPA–821–R–06–012.
15 Samples shall be enumerated by the multiple-tube or multiple-well procedure. Using multiple-tube procedures, employ an appropriate tube
and dilution configuration of the sample as needed and report the Most Probable Number (MPN). Samples tested with Colilert may be enumerated with the multiple-well procedures, Quanti-Tray Quanti-Tray 2000, and the MPN calculated from the table provided by the manufacturer.
16 Colilert-18 is an optimized formulation of the Colilert for the determination of total coliforms and E. coli that provides results within 18 h of
incubation at 35 °C rather than the 24 h required for the Colilert test and is recommended for marine water samples.
17 Descriptions of the Colilert, Colilert-18, Quanti-Tray, and Quanti-Tray/2000 may be obtained from IDEXX Laboratories, Inc., 1 IDEXX
Drive, Westbrook, ME 04092.
18 A description of the mColiBlue24 test, Total Coliforms and E. coli, is available from Hach Company, 100 Dayton Ave., Ames, IA 50010.
19 USEPA. July 2006. Method 1681: Fecal Coliforms in Sewage Sludge (Biosolids) by Multiple-Tube Fermentation using A–1 Medium. U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA–821–R–06–013.
20 Recommended for enumeration of target organism in wastewater effluent.
21 USEPA. July 2006. Method 1603: Escherichia coli (E. coli) in Water by Membrane Filtration Using Modified membrane-Thermotolerant Escherichia coli Agar (modified mTEC). U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA–821–R–06–011.
22 USEPA. July 2006. Method 1682: Salmonella in Sewage Sludge (Biosolids) by Modified Semisolid Rappaport-Vassiliadis (MSRV) Medium.
U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA–821–R–06–014.
23 A description of the Enterolert test may be obtained from IDEXX Laboratories, Inc., 1 IDEXX Drive, Westbrook, ME 04092.
24 USEPA. July 2006. Method 1600: Enterococci in Water by Membrane Filtration Using membrane-Enterococcus Indoxyl-b-D-Glucoside Agar
(mEI). U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA–821–R–06–009.
25 USEPA. October 2002. Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms.
Fifth Edition. U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA/821/R–02/012.
26 USEPA. October 2002. Short-term Methods for Estimating the Chronic Toxicity of Effluents and Receiving Waters to Freshwater Organisms.
Fourth Edition, U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA/821/R–02/013.
27 USEPA. October 2002. Short-term Methods for Estimating the Chronic Toxicity of Effluents and Receiving Waters to Marine and Estuarine
Organisms. Third Edition. U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA/821/R–02/014.
*
*
*
*
*
TABLE IH.—LIST OF APPROVED MICROBIOLOGICAL METHODS FOR AMBIENT WATER
Standard
methods 18th,
19th, 20th Ed.
Standard methods online
AOAC, ASTM,
USGS
9221 B.1/9221
F 11,13.
9223 B 12 .........
9221 B.1–99/
9221 F 11,13.
9223 B–97 12 ...
991.15 10 ..........
1603 20, 1604 21
9222 B/9222
G 18, 9213 D.
..........................
9222 B–97/
9222 G 18.
..........................
MPN 6,8 multiple tube,
..........................
9230 B .............
9230 B–93.
Multiple tube/multiple
well.
MF 2,5,6,7,8 two step ......
Single step, or ..............
Plate count ...................
..........................
..........................
1106.1 23 ..........
1600 24.
p. 143 3.
9230 C .............
Filtration/IMS/FA ...........
Filtration/IMS/FA ...........
1622 25,1623 26.
1623 26.
Method 1
EPA
MPN 6,8,14 multiple tube,
..........................
Multiple tube/multiple
well,
..........................
MF 2,5,6,7,8 two step, or
1103.1 19 ..........
Single step ....................
Parameter and units
Bacteria:
1. E. coli, number
per 100 mL.
2. Enterococci, number per 100 mL.
Protozoa:
3. Cryptosporidium ..
4. Giardia .................
Colilert 12,16
Colilert18 12,15,16.
D5392–93 9.
..........................
mColiBlue24 17.
..........................
D6503–99 9 ......
Enterolert 12,22.
9230 C–93 .......
D5259–92 9.
1 The
method must be specified when results are reported.
0.45 µm membrane filter (MF) or other pore size certified by the manufacturer to fully retain organisms to be cultivated and to be free of
extractables which could interfere with their growth.
3 USEPA. 1978. Microbiological Methods for Monitoring the Environment, Water, and Wastes. Environmental Monitoring and Support Laboratory, U.S. Environmental Protection Agency, Cincinnati, OH. EPA/600/8–78/017.
4 [Reserved]
5 Because the MF technique usually yields low and variable recovery from chlorinated wastewaters, the Most Probable Number method will be
required to resolve any controversies.
6 Tests must be conducted to provide organism enumeration (density). Select the appropriate configuration of tubes/filtrations and dilutions/volumes to account for the quality, character, consistency, and anticipated organism density of the water sample.
2A
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7 When the MF method has not been used previously to test waters with high turbidity, large number of noncoliform bacteria, or samples that
may contain organisms stressed by chlorine, a parallel test should be conducted with a multiple-tube technique to demonstrate applicability and
comparability of results.
8 To assess the comparability of results obtained with individual methods, it is suggested that side-by-side tests be conducted across seasons
of the year with the water samples routinely tested in accordance with the most current Standard Methods for the Examination of Water and
Wastewater or EPA alternate test procedure (ATP) guidelines.
9 ASTM. 2000, 1999, 1996. Annual Book of ASTM Standards—Water and Environmental Technology. Section 11.02. ASTM International. 100
Barr Harbor Drive, West Conshohocken, PA 19428.
10 AOAC. 1995. Official Methods of Analysis of AOAC International, 16th Edition, Volume I, Chapter 17. Association of Official Analytical
Chemists International. 481 North Frederick Avenue, Suite 500, Gaithersburg, MD 20877–2417.
11 The multiple-tube fermentation test is used in 9221B.1. Lactose broth may be used in lieu of lauryl tryptose broth (LTB), if at least 25 parallel
tests are conducted between this broth and LTB using the water samples normally tested, and this comparison demonstrates that the false-positive rate and false-negative rate for total coliform using lactose broth is less than 10 percent. No requirement exists to run the completed phase
on 10 percent of all total coliform-positive tubes on a seasonal basis.
12 These tests are collectively known as defined enzyme substrate tests, where, for example, a substrate is used to detect the enzyme b-glucuronidase produced by E. coli.
13 After prior enrichment in a presumptive medium for total coliform using 9221B.1, all presumptive tubes or bottles showing any amount of
gas, growth or acidity within 48 h ± 3 h of incubation shall be submitted to 9221F. Commercially available EC–MUG media or EC media supplemented in the laboratory with 50 µg/mL of MUG may be used.
14 Samples shall be enumerated by the multiple-tube or multiple-well procedure. Using multiple-tube procedures, employ an appropriate tube
and dilution configuration of the sample as needed and report the Most Probable Number (MPN). Samples tested with Colilert may be enumerated with the multiple-well procedures, Quanti-Tray or Quanti-Tray 2000, and the MPN calculated from the table provided by the manufacturer.
15 Colilert-18 is an optimized formulation of the Colilert for the determination of total coliforms and E. coli that provides results within 18 h of
incubation at 35 °C rather than the 24 h required for the Colilert test and is recommended for marine water samples.
16 Descriptions of the Colilert, Colilert-18, Quanti-Tray, and Quanti-Tray/2000 may be obtained from IDEXX Laboratories, Inc., 1 IDEXX
Drive, Westbrook, ME 04092.
17 A description of the mColiBlue24 test, Total Coliforms and E. coli, is available from Hach Company, 100 Dayton Ave., Ames, IA 50010.
18 Subject total coliform positive samples determined by 9222B or other membrane filter procedure to 9222G using NA–MUG media.
19 USEPA. July 2006. Method 1103.1: Escherichia coli (E. coli) in Water by Membrane Filtration Using membrane-Thermotolerant Escherichia
coli Agar (mTEC). U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA–821–R–06–010.
20 USEPA. July 2006. Method 1603: Escherichia coli (E. coli) in Water by Membrane Filtration Using Modified membrane-Thermotolerant Escherichia coli Agar (Modified mTEC). U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA–821–R–06–011.
21 Preparation and use of MI agar with a standard membrane filter procedure is set forth in the article, Brenner et al. 1993. ‘‘New Medium for
the Simultaneous Detection of Total Coliform and Escherichia coli in Water.’’ Appl. Environ. Microbiol. 59:3534–3544 and in USEPA. September
2002.: Method 1604: Total Coliforms and Escherichia coli (E. coli) in Water by Membrane Filtration by Using a Simultaneous Detection Technique (MI Medium). U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA 821–R–02–024.
22 A description of the Enterolert test may be obtained from IDEXX Laboratories, Inc., 1 IDEXX Drive, Westbrook, ME 04092.
23 USEPA. July 2006. Method 1106.1: Enterococci in Water by Membrane Filtration Using membrane-Enterococcus-Esculin Iron Agar (mE–
EIA). U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA–821–R–06–008.
24 USEPA. July 2006. Method 1600: Enterococci in Water by Membrane Filtration Using membrane-Enterococcus Indoxyl-b-D-Glucoside Agar
(mEI). U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA–821–R–06–009.
25 Method 1622 uses filtration, concentration, immunomagnetic separation of oocysts from captured material, immunofluorescence assay to determine concentrations, and confirmation through vital dye staining and differential interference contrast microscopy for the detection of
Cryptosporidium. USEPA. 2001. Method 1622: Cryptosporidium in Water by Filtration/IMS/FA. U.S. Environmental Protection Agency, Office of
Water, Washington, DC EPA–821–R–01–026.
26 Method 1623 uses filtration, concentration, immunomagnetic separation of oocysts and cysts from captured material, immunofluorescence
assay to determine concentrations, and confirmation through vital dye staining and differential interference contrast microscopy for the simultaneous detection of Cryptosporidium and Giardia oocysts and cysts. USEPA. 2001. Method 1623. Cryptosporidium and Giardia in Water by Filtration/IMS/FA. U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA–821–R–01–025.
(b) The full texts of the methods from
the following references which are cited
in Tables IA, IB, IC, ID, IE, IF, IG and
IH are incorporated by reference into
this regulation and may be obtained
from the source identified. All costs
cited are subject to change and must be
verified from the indicated source. The
full texts of all the test procedures cited
are available for inspection at the
National Archives and Records
Administration (NARA). For
information on the availability of this
material at NARA, call 202–741–6030,
or go to: https://www.archives.gov/
federal_register/
code_of_federal_regulations/
ibr_locations.html.
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References, Sources, Costs, and Table
Citations
*
*
*
*
*
(2) USEPA. 1978. Microbiological
Methods for Monitoring the
Environment, Water, and Wastes.
Environmental Monitoring and Support
Laboratory, U.S. Environmental
VerDate Aug<31>2005
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Protection Agency, Cincinnati, Ohio.
EPA/600/8–78/017. Available at https://
www.epa.gov/clariton/srch.htm or from:
National Technical Information Service,
5285 Port Royal Road, Springfield,
Virginia 22161, Pub. No. PB–290329/
A.S. Table IA, Note 3; Table IH, Note 3.
*
*
*
*
*
(6) American Public Health
Association. 1992, 1995, and 1998.
Standard Methods for the Examination
of Water and Wastewater. 18th, 19th,
and 20th Edition (respectively).
Available from: American Public Health
Association, 1015 15th Street, NW.,
Washington, DC 20005. Standard
Methods Online is available through the
Standard Methods Web site (https://
www.standardmethods.org). Tables IA,
IB, IC, ID, IE, and IH.
*
*
*
*
*
(10) ASTM International. Annual
Book of ASTM Standards, Water, and
Environmental Technology, Section 11,
Volumes 11.01 and 11.02, 1994, 1996,
1999, Volume 11.02, 2000, and
individual standards published after
PO 00000
Frm 00010
Fmt 4701
Sfmt 4700
2000. Available from: ASTM
International, 100 Barr Harbor Drive,
P.O. Box C700, West Conshohocken, PA
19428–2959, or https://www.astm.org.
Tables IA, IB, IC, ID, IE, and IH.
*
*
*
*
*
(11) USGS. 1989. U.S. Geological
Survey Techniques of Water-Resources
Investigations, Book 5, Laboratory
Analysis, Chapter A4, Methods for
Collection and Analysis of Aquatic
Biological and Microbiological Samples,
U.S. Geological Survey, U.S.
Department of the Interior, Reston,
Virginia. Available from USGS Books
and Open-File Reports Section, Federal
Center, Box 25425, Denver, Colorado
80225. Table IA, Note 5; Table IH.
*
*
*
*
*
(34) USEPA. October 2002. Methods
for Measuring the Acute Toxicity of
Effluents and Receiving Waters to
Freshwater and Marine Organisms. Fifth
Edition. U.S. Environmental Protection
Agency, Office of Water, Washington,
DC EPA 821–R–02–012. Available at
https://www.epa.gov/epahome/index/
E:\FR\FM\26MRR2.SGM
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sources.htm or from National Technical
Information Service, 5285 Port Royal
Road, Springfield, Virginia 22161, Pub.
No. PB2002–108488. Table IA, Note 25.
*
*
*
*
*
(38) USEPA. October 2002. ShortTerm Methods for Measuring the
Chronic Toxicity of Effluents and
Receiving Waters to Freshwater
Organisms. Fourth Edition. U.S.
Environmental Protection Agency,
Office of Water, Washington, DC EPA
821–R–02–013. Available at https://
www.epa.gov/epahome/index/
sources.htm or from National Technical
Information Service, 5285 Port Royal
Road, Springfield, Virginia 22161, Pub.
No. PB2002–108489. Table IA, Note 26.
(39) USEPA. October 2002. ShortTerm Methods for Measuring the
Chronic Toxicity of Effluents and
Receiving Waters to Marine and
Estuarine Organisms. Third Edition.
U.S. Environmental Protection Agency,
Office of Water, Washington, DC EPA
821–R–02–014. Available at https://
www.epa.gov/epahome/index/
sources.htm or from National Technical
Information Service, 5285 Port Royal
Road, Springfield, Virginia 22161, Pub.
No. PB2002–108490. Table IA, Note 27.
*
*
*
*
*
(52) IDEXX Laboratories, Inc. 2002.
Description of Colilert, Colilert-18,
Quanti-Tray, Quanti-Tray/2000,
Enterolert methods are available from
IDEXX Laboratories, Inc., One Idexx
Drive, Westbrook, Maine 04092. Table
IA, Notes 17 and 23; Table IH, Notes 16
and 22.
(53) Hach Company, Inc. Revision 2,
1999. Description of m-ColiBlue24
Method, Total Coliforms and E. coli, is
available from Hach Company, 100
Dayton Ave, Ames IA 50010. Table IA,
Note 18; Table IH, Note 17.
(54) USEPA. July 2006. Method
1103.1: Escherichia coli (E. coli) in
Water by Membrane Filtration Using
membrane-Thermotolerant Escherichia
coli Agar (mTEC). U.S. Environmental
Protection Agency, Office of Water,
Washington DC EPA–621–R–06–010.
Available at https://www.epa.gov/
waterscience/methods/. Table IH, Note
19.
(55) USEPA. July 2006. Method
1106.1: Enterococci in Water by
Membrane Filtration Using membraneEnterococcus-Esculin Iron Agar (mE–
EIA). U.S. Environmental Protection
Agency, Office of Water, Washington DC
EPA–621–R–06–008. Available at
VerDate Aug<31>2005
15:34 Mar 23, 2007
Jkt 211001
https://www.epa.gov/waterscience/
methods/. Table IH, Note 23
(56) USEPA. July 2006. Method 1603:
Escherichia coli (E. coli) in Water by
Membrane Filtration Using Modified
membrane-Thermotolerant Escherichia
coli Agar (Modified mTEC). U.S.
Environmental Protection Agency,
Office of Water, Washington DC EPA–
821–R–06–011. Available at https://
www.epa.gov/waterscience/methods/.
Table IH, Note 19; Table IH, Note 20.
(57) Brenner et al. 1993. New Medium
for the Simultaneous Detection of Total
Coliforms and Escherichia coli in Water.
Appl. Environ. Microbiol. 59:3534–
3544. Available from the American
Society for Microbiology, 1752 N Street
NW., Washington DC 20036. Table IH,
Note 21.
(58) USEPA. September 2002. Method
1604: Total Coliforms and Escherichia
coli (E. coli) in Water by Membrane
Filtration Using a Simultaneous
Detection Technique (MI Medium). U.S.
Environmental Protection Agency,
Office of Water, Washington DC EPA–
821–R–02–024. Available at https://
www.epa.gov/waterscience/methods/.
Table IH, Note 20.
(59) USEPA. July 2006. Method 1600:
Enterococci in Water by Membrane
Filtration Using membraneEnterococcus Indoxyl-b-D-Glucoside
Agar (mEI). U.S. Environmental
Protection Agency, Office of Water,
Washington DC EPA–821–R–06–009.
Available at https://www.epa.gov/
waterscience/methods/. Table IA, Note
24; Table IH, Note 24.
(60) USEPA. April 2001. Method
1622: Cryptosporidium in Water by
Filtration/IMS/FA. U.S. Environmental
Protection Agency, Office of Water,
Washington DC EPA–821–R–01–026.
Available at https://www.epa.gov/
waterscience/methods/. Table IH, Note
25.
(61) USEPA. April 2001. Method
1623: Cryptosporidium and Giardia in
Water by Filtration/IMS/FA. U.S.
Environmental Protection Agency,
Office of Water, Washington DC. EPA–
821–R–01–025. Available at https://
www.epa.gov/waterscience/methods/.
Table IH, Note 26.
(62) AOAC. 1995. Official Methods of
Analysis of AOAC International, 16th
Edition, Volume I, Chapter 17. AOAC
International, 481 North Frederick
Avenue, Suite 500, Gaithersburg,
Maryland 20877–2417. Table IA, Note
11; Table IH.
*
*
*
*
*
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(70) USEPA. July 2006. Method 1680:
Fecal Coliforms in Sewage Sludge
(Biosolids) by Multiple-Tube
Fermentation using Lauryl Tryptose
Broth (LTB) and EC Medium. U.S.
Environmental Protection Agency,
Office of Water, Washington DC. EPA
821–R–06–012. Available at https://
www.epa.gov/waterscience/methods/.
(71) USEPA. July 2006. Method 1681:
Fecal Coliforms in Sewage Sludge
(Biosolids) by Multiple-Tube
Fermentation using A–1 Medium. U.S.
Environmental Protection Agency,
Office of Water, Washington DC. EPA
821–R–06–013. Available at https://
www.epa.gov/waterscience/methods/.
(72) USEPA. July 2006. Method 1682:
Salmonella in Sewage Sludge
(Biosolids) by Modified Semisolid
Rappaport-Vassiliadis (MSRV) Medium.
U.S. Environmental Protection Agency,
Office of Water, Washington DC. EPA
821–R–06–014. Available at https://
www.epa.gov/waterscience/methods/.
*
*
*
*
*
(e) Sample preservation procedures,
container materials, and maximum
allowable holding times for parameters
are cited in Tables IA, IB, IC, ID, IE, IF,
IG and IH are prescribed in Table II.
Information in the table takes
precedence over information in specific
methods or elsewhere. Any person may
apply for a variance from the prescribed
preservation techniques, container
materials, and maximum holding times
applicable to samples taken from a
specific discharge. Applications for
variances may be made by letters to the
Regional Administrator in the Region in
which the discharge will occur.
Sufficient data should be provided to
assure such variance does not adversely
affect the integrity of the sample. Such
data will be forwarded by the Regional
Administrator, to the Alternate Test
Procedure Program Coordinator,
Washington, DC, for technical review
and recommendations for action on the
variance application. Upon receipt of
the recommendations from the Alternate
Test Procedure Program Coordinator,
the Regional Administrator may grant a
variance applicable to the specific
discharge to the applicant. A decision to
approve or deny a variance will be made
within 90 days of receipt of the
application by the Regional
Administrator.
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TABLE II.—REQUIRED CONTAINERS, PRESERVATION TECHNIQUES, AND HOLDING TIMES
Parameter No./name
Container
Table IA—Bacterial Tests:
1–5. Coliform, total, fecal, and E. coli ..............
6. Fecal streptococci ........................................
7. Enterococci ...................................................
8. Salmonella ....................................................
Table IA—Aquatic Toxicity Tests:
9–11. Toxicity, acute and chronic ....................
Table lB—Inorganic Tests:
1. Acidity ...........................................................
2. Alkalinity .......................................................
4. Ammonia ......................................................
9. Biochemical oxygen demand .......................
10. Boron ..........................................................
11. Bromide ......................................................
14. Biochemical oxygen demand, carbonaceous.
15. Chemical oxygen demand ..........................
16. Chloride ......................................................
17. Chlorine, total residual ...............................
PA,
PA,
PA,
PA,
G
G
G
G
1
2,3
Preservation
.............................
.............................
.............................
.............................
Cool,
Cool,
Cool,
Cool,
<10 °C,
<10 °C,
<10 °C,
<10 °C,
0.0008%
0.0008%
0.0008%
0.0008%
Na2S2O3 5
Na2S2O3 5
Na2S2O3 5
Na2S2O3 5
Maximum holding time
....
....
....
....
6
6
6
6
hours.22,23
hours.22
hours.22
hours.22
P, FP, G ........................
Cool, ≤6 °C 16 .....................................
36 hours.
P,
P,
P,
P,
P,
P,
P,
FP, G ........................
FP, G ........................
FP, G ........................
FP, G ........................
FP, or Quartz ............
FP, G ........................
FP G .........................
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18, H2SO4 to pH<2 .........
Cool, ≤6 °C 18 .....................................
HNO3 to pH<2 ...................................
None required ....................................
Cool, ≤6 °C 18 .....................................
14 days.
14 days.
28 days.
48 hours.
6 months.
28 days.
48 hours.
P, FP, G ........................
P, FP, G ........................
P, G ...............................
Cool, ≤6 °C 18, H2SO4 to pH<2 .........
None required ....................................
None required ....................................
21. Color ...........................................................
23–24. Cyanide, total or available (or CATC) ..
P, FP, G ........................
P, FP, G ........................
P ....................................
P, FP, G ........................
P, FP, G ........................
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18, NaOH to pH>12 6, reducing agent 5.
None required ....................................
HNO3 or H2SO4 to pH<2 ..................
None required ....................................
28 days.
28 days.
Analyze within 15 minutes.
48 hours.
14 days.
25. Fluoride .......................................................
27. Hardness ....................................................
28. Hydrogen ion (pH) ......................................
31, 43. Kjeldahl and organic N .........................
Table IB—Metals: 7
18. Chromium VI ..............................................
35. Mercury (CVAA) .........................................
35. Mercury (CVAFS) .......................................
P, FP, G ........................
Cool, ≤6 °C 18, H2SO4 to pH<2 .........
28 days.
6 months.
Analyze within 15 minutes.
28 days.
P, FP, G ........................
P, FP, G ........................
FP, G; and FP-lined
cap 17.
P, FP, G ........................
Cool, ≤6 °C 18, pH = 9.3–9.7 20 ..........
HNO3 to pH<2 ...................................
5 mL/L 12N HCl or 5 mL/L BrCl 17 ....
28 days.
28 days.
90 days.17
HNO3 to pH<2, or at least 24 hours
prior to analysis 19.
6 months.
P, FP, G ........................
P, FP, G ........................
P, FP, G ........................
G ....................................
48
28
48
28
3, 5–8, 12, 13, 19, 20, 22, 26, 29, 30, 32–34,
36, 37, 45, 47, 51, 52, 58–60, 62, 63, 70–
72, 74, 75.
Metals, except boron, chromium VI, and mercury.
38. Nitrate .........................................................
39. Nitrate-nitrite ...............................................
40. Nitrite ..........................................................
41. Oil and grease ............................................
42. Organic Carbon ..........................................
P, FP, G ........................
44. Orthophosphate ..........................................
P, FP, G ........................
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18, H2SO4 to pH<2 .........
Cool, ≤6 °C 18 .....................................
Cool to ≤6 °C 18, HCl or H2SO4 to
pH<2.
Cool to ≤6 °C 18, HCl, H2SO4, or
H3PO4 to pH<2.
Cool, ≤6 °C 18 .....................................
46. Oxygen, Dissolved Probe ...........................
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G, Bottle and top ...........
None required ....................................
47.
48.
49.
50.
53.
54.
55.
56.
57.
61.
64.
65.
66.
Winkler ........................................................
Phenols .......................................................
Phosphorous (elemental) ...........................
Phosphorous, total .....................................
Residue, total .............................................
Residue, Filterable .....................................
Residue, Nonfilterable (TSS) .....................
Residue, Settleable ....................................
Residue, Volatile ........................................
Silica ...........................................................
Specific conductance .................................
Sulfate ........................................................
Sulfide .........................................................
G, Bottle and top ...........
G ....................................
G ....................................
P, FP, G ........................
P, FP, G ........................
P, FP, G ........................
P, FP, G ........................
P, FP, G ........................
P, FP, G ........................
P or Quartz ....................
P, FP, G ........................
P, FP, G ........................
P, FP, G ........................
67. Sulfite ..........................................................
P, FP, G ........................
Fix on site and store in dark .............
Cool, ≤6 °C 18, H2SO4 to pH<2 .........
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18, H2SO4 to pH<2 .........
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18 .....................................
Cool, ≤6 °C 18, add zinc acetate plus
sodium hydroxide to pH>9.
None required ....................................
68. Surfactants .................................................
69. Temperature ...............................................
73. Turbidity ......................................................
Table lC—Organic Tests 8
P, FP, G ........................
P, FP, G ........................
P, FP, G ........................
Cool, ≤6 °C 18 .....................................
None required ....................................
Cool, ≤6 °C 18 .....................................
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hours.
days.
hours.
days.
28 days.
Filter within 15 minutes;
Analyze within 48
hours.
Analyze within 15 minutes.
8 hours.
28 days.
48 hours.
28 days.
7 days.
7 days.
7 days.
48 hours.
7 days.
28 days.
28 days.
28 days.
7 days.
Analyze within 15 minutes.
48 hours.
Analyze.
48 hours.
Federal Register / Vol. 72, No. 57 / Monday, March 26, 2007 / Rules and Regulations
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TABLE II.—REQUIRED CONTAINERS, PRESERVATION TECHNIQUES, AND HOLDING TIMES—Continued
Parameter No./name
Container
1
Preservation
2,3
Maximum holding time
13, 18–20, 22, 24–28, 34–37, 39–43, 45–47,
56, 76, 104, 105, 108–111, 113. Purgeable
Halocarbons.
6, 57, 106. Purgeable aromatic hydrocarbons
G, FP-lined septum .......
Cool, ≤6 °C 18, 0.008% Na2S2O3 5 ....
14 days.
G, FP-lined septum .......
14 days.9
3, 4. Acrolein and acrylonitrile ..........................
G, FP-lined septum .......
23, 30, 44, 49, 53, 77, 80, 81, 98, 100, 112.
Phenols 11.
G, FP-lined cap .............
Cool, ≤6 °C 18, 0.008% Na2S2O3 5,
HCl to pH 2 9.
Cool, ≤6 °C 18, 0.008% Na2S2O3 5,
pH to 4–5 10.
Cool, ≤6 °C 18, 0.008% Na2S2O3 5 ....
7, 38. Benzidines 11, 12 .....................................
14, 17, 48, 50–52. Phthalate esters 11 .............
G, FP-lined cap .............
G, FP-lined cap .............
Cool, ≤6 °C 18, 0.008% Na2S2O3 5 ....
Cool, ≤6 °C 18 .....................................
82–84. Nitrosamines 11,
................................
G, FP-lined cap .............
Cool, ≤6 °C 18, store in dark, 0.008%
Na2S2O3 5.
88–94. PCBs 11 .................................................
G, FP-lined cap .............
Cool, ≤6 °C 18 .....................................
54, 55, 75,
isophorone 11.
and
G, FP-lined cap .............
Cool, ≤6 °C 18, store in dark, 0.008%
Na2S2O3 5.
1, 2, 5, 8–12, 32, 33, 58, 59, 74, 78, 99, 101.
Polynuclear aromatic hydrocarbons 11.
G, FP-lined cap .............
Cool, ≤6 °C 18, store in dark, 0.008%
Na2S2O3 5.
15, 16, 21, 31, 87. Haloethers 11 ......................
G, FP-lined cap .............
Cool, ≤6 °C 18, 0.008% Na2S2O3 5 ....
29, 35–37, 63–65, 107. Chlorinated hydrocarbons 11.
G, FP-lined cap .............
Cool, ≤6 °C 18 .....................................
G ....................................
1 year.
G ....................................
Cool, ≤6 °C 18, 0.008% Na2S2O3 5,
pH<9.
Cool, ≤6 °C 18 .....................................
G ....................................
G ....................................
Cool, ≤6 °C 18 .....................................
Freeze, ≤¥10 °C ...............................
24 hours.
1 year.
G, FP-lined cap .............
Cool, ≤6 °C 18, pH 5–9 15 ...................
7 days until extraction,
40 days after extraction.
P, FP, G ........................
HNO3 to pH<2 ...................................
6 months.
PA, G .............................
PA, G .............................
Cool, <10 °C, 0.0008% Na2S2O3 5 ....
Cool, <10 °C, 0.0008% Na2S2O3 5 ....
6 hours.22
6 hours.22
LDPE; field filtration .......
LDPE; field filtration .......
0–8 °C ................................................
0–8 °C ................................................
96 hours.21
96 hours.21
79.
14
Nitroaromatics
60–62, 66–72, 85, 86, 95–97, 102, 103.
CDDs/CDFs 11.
Aqueous Samples: Field and Lab Preservation
Solids and Mixed-Phase Samples: Field Preservation.
Tissue Samples: Field Preservation .................
Solids, Mixed-Phase, and Tissue Samples:
Lab Preservation.
Table lD—Pesticides Tests:
1–70. Pesticides 11 ...........................................
Table IE—Radiological Tests:
1–5. Alpha, beta, and radium ...........................
Table IH—Bacterial Tests:
1. E. coli ............................................................
2. Enterococci ...................................................
Table IH—Protozoan Tests:
8. Cryptosporidium ...........................................
9. Giardia ..........................................................
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4
14 days.10
7 days until extraction,
40 days after extraction.
7 days until extraction.13
7 days until extraction,
40 days after extraction.
7 days until extraction,
40 days after extraction.
1 year until extraction, 1
year after extraction.
7 days until extraction,
40 days after extraction.
7 days until extraction,
40 days after extraction.
7 days until extraction,
40 days after extraction.
7 days until extraction,
40 days after extraction.
7 days.
1 ‘‘P’’ is polyethylene; ‘‘FP’’ is fluoropolymer (polytetrafluoroethylene (PTFE; Teflon), or other fluoropolymer, unless stated otherwise in this
Table II; ‘‘G’’ is glass; ‘‘PA’’ is any plastic that is made of a sterlizable material (polypropylene or other autoclavable plastic); ‘‘LDPE’’ is low density polyethylene.
2 Except where noted in this Table II and the method for the parameter, preserve each grab sample within 15 minutes of collection. For a composite sample collected with an automated sampler (e.g., using a 24-hour composite sampler; see 40 CFR 122.21(g)(7)(i) or 40 CFR Part 403,
Appendix E), refrigerate the sample at ≤6 °C during collection unless specified otherwise in this Table II or in the method(s). For a composite
sample to be split into separate aliquots for preservation and/or analysis, maintain the sample at ≤6 °C, unless specified otherwise in this Table II
or in the method(s), until collection, splitting, and preservation is completed. Add the preservative to the sample container prior to sample collection when the preservative will not compromise the integrity of a grab sample, a composite sample, or an aliquot split from a composite sample;
otherwise, preserve the grab sample, composite sample, or aliquot split from a composite sample within 15 minutes of collection. If a composite
measurement is required but a composite sample would compromise sample integrity, individual grab samples must be collected at prescribed
time intervals (e.g., 4 samples over the course of a day, at 6-hour intervals). Grab samples must be analyzed separately and the concentrations
averaged. Alternatively, grab samples may be collected in the field and composited in the laboratory if the compositing procedure produces results equivalent to results produced by arithmetic averaging of the results of analysis of individual grab samples. For examples of laboratory
compositing procedures, see EPA Method 1664A (oil and grease) and the procedures at 40 CFR 141.34(f)(14)(iv) and (v) (volatile organics).
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3 When any sample is to be shipped by common carrier or sent via the U.S. Postal Service, it must comply with the Department of Transportation Hazardous Materials Regulations (49 CFR Part 172). The person offering such material for transportation is responsible for ensuring such
compliance. For the preservation requirements of Table II, the Office of Hazardous Materials, Materials Transportation Bureau, Department of
Transportation has determined that the Hazardous Materials Regulations do not apply to the following materials: Hydrochloric acid (HCl) in water
solutions at concentrations of 0.04% by weight or less (pH about 1.96 or greater); Nitric acid (HNO3) in water solutions at concentrations of
0.15% by weight or less (pH about 1.62 or greater); Sulfuric acid (H2SO4) in water solutions at concentrations of 0.35% by weight or less (pH
about 1.15 or greater); and Sodium hydroxide (NaOH) in water solutions at concentrations of 0.080% by weight or less (pH about 12.30 or less).
4 Samples should be analyzed as soon as possible after collection. The times listed are the maximum times that samples may be held before
the start of analysis and still be considered valid (e.g., samples analyzed for fecal coliforms may be held up to 6 hours prior to commencing analysis). Samples may be held for longer periods only if the permittee or monitoring laboratory has data on file to show that, for the specific types of
samples under study, the analytes are stable for the longer time, and has received a variance from the Regional Administrator under § 136.3(e).
For a grab sample, the holding time begins at the time of collection. For a composite sample collected with an automated sampler (e.g., using a
24-hour composite sampler; see 40 CFR 122.21(g)(7)(i) or 40 CFR Part 403, Appendix E), the holding time begins at the time of the end of collection of the composite sample. For a set of grab samples composited in the field or laboratory, the holding time begins at the time of collection
of the last grab sample in the set. Some samples may not be stable for the maximum time period given in the table. A permittee or monitoring
laboratory is obligated to hold the sample for a shorter time if it knows that a shorter time is necessary to maintain sample stability. See
§ 136.3(e) for details. The date and time of collection of an individual grab sample is the date and time at which the sample is collected. For a
set of grab samples to be composited, and that are all collected on the same calendar date, the date of collection is the date on which the samples are collected. For a set of grab samples to be composited, and that are collected across two calendar dates, the date of collection is the
dates of the two days; e.g., November 14–15. For a composite sample collected automatically on a given date, the date of collection is the date
on which the sample is collected. For a composite sample collected automatically, and that is collected across two calendar dates, the date of
collection is the dates of the two days; e.g., November 14–15.
5 Add a reducing agent only if an oxidant (e.g., chlorine) is present. Reducing agents shown to be effective are sodium thiosulfate (Na S O ),
2 2 3
ascorbic acid, sodium arsenite (NaAsO2), or sodium borohydride (NaBH4). However, some of these agents have been shown to produce a positive or negative cyanide bias, depending on other substances in the sample and the analytical method used. Therefore, do not add an excess of
reducing agent. Methods recommending ascorbic acid (e.g., EPA Method 335.4) specify adding ascorbic acid crystals, 0.1–0.6 g, until a drop of
sample produces no color on potassium iodide (KI) starch paper, then adding 0.06 g (60 mg) for each liter of sample volume. If NaBH4 or
NaAsO2 is used, 25 mg/L NaBH4 or 100 mg/L NaAsO2 will reduce more than 50 mg/L of chlorine (see method ‘‘Kelada-01’’ and/or Standard
Method 4500–CN¥ for more information). After adding reducing agent, test the sample using KI paper, a test strip (e.g. for chlorine, SenSafeTM
Total Chlorine Water Check 480010) moistened with acetate buffer solution (see Standard Method 4500–Cl.C.3e), or a chlorine/oxidant test
method (e.g., EPA Method 330.4 or 330.5), to make sure all oxidant is removed. If oxidant remains, add more reducing agent. Whatever agent is
used, it should be tested to assure that cyanide results are not affected adversely.
6 Sample collection and preservation: Collect a volume of sample appropriate to the analytical method in a bottle of the material specified. If
the sample can be analyzed within 48 hours and sulfide is not present, adjust the pH to > 12 with sodium hydroxide solution (e.g., 5% w/v), refrigerate as specified, and analyze within 48 hours. Otherwise, to extend the holding time to 14 days and mitigate interferences, treat the sample
immediately using any or all of the following techniques, as necessary, followed by adjustment of the sample pH to > 12 and refrigeration as
specified. There may be interferences that are not mitigated by approved procedures. Any procedure for removal or suppression of an interference may be employed, provided the laboratory demonstrates that it more accurately measures cyanide. Particulate cyanide (e.g., ferric ferrocyanide) or a strong cyanide complex (e.g., cobalt cyanide) are more accurately measured if the laboratory holds the sample at room temperature and pH > 12 for a minimum of 4 hours prior to analysis, and performs UV digestion or dissolution under alkaline (pH=12) conditions, if necessary.
(1) Sulfur: To remove elemental sulfur (S8), filter the sample immediately. If the filtration time will exceed 15 minutes, use a larger filter or a
method that requires a smaller sample volume (e.g., EPA Method 335.4 or Lachat Method 01). Adjust the pH of the filtrate to > 12 with NaOH,
refrigerate the filter and filtrate, and ship or transport to the laboratory. In the laboratory, extract the filter with 100 mL of 5% NaOH solution for a
minimum of 2 hours. Filter the extract and discard the solids. Combine the 5% NaOH-extracted filtrate with the initial filtrate, lower the pH to approximately 12 with concentrated hydrochloric or sulfuric acid, and analyze the combined filtrate. Because the detection limit for cyanide will be
increased by dilution by the filtrate from the solids, test the sample with and without the solids procedure if a low detection limit for cyanide is
necessary. Do not use the solids procedure if a higher cyanide concentration is obtained without it. Alternatively, analyze the filtrates from the
sample and the solids separately, add the amounts determined (in µg or mg), and divide by the original sample volume to obtain the cyanide
concentration.
(2) Sulfide: If the sample contains sulfide as determined by lead acetate paper, or if sulfide is known or suspected to be present, immediately
conduct one of the volatilization treatments or the precipitation treatment as follows: Volatilization—Headspace expelling. In a fume hood or wellventilated area, transfer 0.75 liter of sample to a 4.4 L collapsible container (e.g., CubitainerTM). Acidify with concentrated hydrochloric acid to pH
< 2. Cap the container and shake vigorously for 30 seconds. Remove the cap and expel the headspace into the fume hood or open area by collapsing the container without expelling the sample. Refill the headspace by expanding the container. Repeat expelling a total of five headspace
volumes. Adjust the pH to > 12, refrigerate, and ship or transport to the laboratory. Scaling to a smaller or larger sample volume must maintain
the air to sample volume ratio. A larger volume of air will result in too great a loss of cyanide (> 10%). Dynamic stripping: In a fume hood or wellventilated area, transfer 0.75 liter of sample to a container of the material specified and acidify with concentrated hydrochloric acid to pH < 2.
Using a calibrated air sampling pump or flowmeter, purge the acidified sample into the fume hood or open area through a fritted glass aerator at
a flow rate of 2.25 L/min for 4 minutes. Adjust the pH to > 12, refrigerate, and ship or transport to the laboratory. Scaling to a smaller or larger
sample volume must maintain the air to sample volume ratio. A larger volume of air will result in too great a loss of cyanide (> 10%). Precipitation: If the sample contains particulate matter that would be removed by filtration, filter the sample prior to treatment to assure that cyanide associated with the particulate matter is included in the measurement. Ship or transport the filter to the laboratory. In the laboratory, extract the filter
with 100 mL of 5% NaOH solution for a minimum of 2 hours. Filter the extract and discard the solids. Combine the 5% NaOH-extracted filtrate
with the initial filtrate, lower the pH to approximately 12 with concentrated hydrochloric or sulfuric acid, and analyze the combined filtrate. Because the detection limit for cyanide will be increased by dilution by the filtrate from the solids, test the sample with and without the solids procedure if a low detection limit for cyanide is necessary. Do not use the solids procedure if a higher cyanide concentration is obtained without it. Alternatively, analyze the filtrates from the sample and the solids separately, add the amounts determined (in µg or mg), and divide by the original
sample volume to obtain the cyanide concentration. For removal of sulfide by precipitation, raise the pH of the sample to > 12 with NaOH solution, then add approximately 1 mg of powdered cadmium chloride for each mL of sample. For example, add approximately 500 mg to a 500-mL
sample. Cap and shake the container to mix. Allow the precipitate to settle and test the sample with lead acetate paper. If necessary, add cadmium chloride but avoid adding an excess. Finally, filter through 0.45 micron filter. Cool the sample as specified and ship or transport the filtrate
and filter to the laboratory. In the laboratory, extract the filter with 100 mL of 5% NaOH solution for a minimum of 2 hours. Filter the extract and
discard the solids. Combine the 5% NaOH-extracted filtrate with the initial filtrate, lower the pH to approximately 12 with concentrated hydrochloric or sulfuric acid, and analyze the combined filtrate. Because the detection limit for cyanide will be increased by dilution by the filtrate from
the solids, test the sample with and without the solids procedure if a low detection limit for cyanide is necessary. Do not use the solids procedure
if a higher cyanide concentration is obtained without it. Alternatively, analyze the filtrates from the sample and the solids separately, add the
amounts determined (in µg or mg), and divide by the original sample volume to obtain the cyanide concentration. If a ligand-exchange method is
used (e.g., ASTM D6888), it may be necessary to increase the ligand-exchange reagent to offset any excess of cadmium chloride.
(3) Sulfite, thiosulfate, or thiocyanate: If sulfite, thiosulfate, or thiocyanate is known or suspected to be present, use UV digestion with a glass
coil (Method Kelada-01) or ligand exchange (Method OIA–1677) to preclude cyanide loss or positive interference.
(4) Aldehyde: If formaldehyde, acetaldehyde, or another water-soluble aldehyde is known or suspected to be present, treat the sample with 20
mL of 3.5% ethylenediamine solution per liter of sample.
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(5) Carbonate: Carbonate interference is evidenced by noticeable effervescence upon acidification in the distillation flask, a reduction in the pH
of the absorber solution, and incomplete cyanide spike recovery. When significant carbonate is present, adjust the pH to ≥12 using calcium hydroxide instead of sodium hydroxide. Allow the precipitate to settle and decant or filter the sample prior to analysis (also see Standard Method
4500–CN.B.3.d).
(6) Chlorine, hypochlorite, or other oxidant: Treat a sample known or suspected to contain chlorine, hypochlorite, or other oxidant as directed
in footnote 5.
7 For dissolved metals, filter grab samples within 15 minutes of collection and before adding preservatives. For a composite sample collected
with an automated sampler (e.g., using a 24-hour composite sampler; see 40 CFR 122.21(g)(7)(i) or 40 CFR Part 403, Appendix E), filter the
sample within 15 minutes after completion of collection and before adding preservatives. If it is known or suspected that dissolved sample integrity will be compromised during collection of a composite sample collected automatically over time (e.g., by interchange of a metal between dissolved and suspended forms), collect and filter grab samples to be composited (footnote 2) in place of a composite sample collected automatically.
8 Guidance applies to samples to be analyzed by GC, LC, or GC/MS for specific compounds.
9 If the sample is not adjusted to pH 2, then the sample must be analyzed within seven days of sampling.
10 The pH adjustment is not required if acrolein will not be measured. Samples for acrolein receiving no pH adjustment must be analyzed within 3 days of sampling.
11 When the extractable analytes of concern fall within a single chemical category, the specified preservative and maximum holding times
should be observed for optimum safeguard of sample integrity (i.e., use all necessary preservatives and hold for the shortest time listed). When
the analytes of concern fall within two or more chemical categories, the sample may be preserved by cooling to ≤6 °C, reducing residual chlorine
with 0.008% sodium thiosulfate, storing in the dark, and adjusting the pH to 6–9; samples preserved in this manner may be held for seven days
before extraction and for forty days after extraction. Exceptions to this optional preservation and holding time procedure are noted in footnote 5
(regarding the requirement for thiosulfate reduction), and footnotes 12, 13 (regarding the analysis of benzidine).
12 If 1,2-diphenylhydrazine is likely to be present, adjust the pH of the sample to 4.0 ± 0.2 to prevent rearrangement to benzidine.
13 Extracts may be stored up to 30 days at < 0 °C.
14 For the analysis of diphenylnitrosamine, add 0.008% Na S O and adjust pH to 7–10 with NaOH within 24 hours of sampling.
2 2 3
15 The pH adjustment may be performed upon receipt at the laboratory and may be omitted if the samples are extracted within 72 hours of collection. For the analysis of aldrin, add 0.008% Na2S2O3.
16 Sufficient ice should be placed with the samples in the shipping container to ensure that ice is still present when the samples arrive at the
laboratory. However, even if ice is present when the samples arrive, it is necessary to immediately measure the temperature of the samples and
confirm that the preservation temperature maximum has not been exceeded. In the isolated cases where it can be documented that this holding
temperature cannot be met, the permittee can be given the option of on-site testing or can request a variance. The request for a variance should
include supportive data which show that the toxicity of the effluent samples is not reduced because of the increased holding temperature.
17 Samples collected for the determination of trace level mercury (<100 ng/L) using EPA Method 1631 must be collected in tightly-capped
fluoropolymer or glass bottles and preserved with BrCl or HCl solution within 48 hours of sample collection. The time to preservation may be extended to 28 days if a sample is oxidized in the sample bottle. A sample collected for dissolved trace level mercury should be filtered in the laboratory within 24 hours of the time of collection. However, if circumstances preclude overnight shipment, the sample should be filtered in a designated clean area in the field in accordance with procedures given in Method 1669. If sample integrity will not be maintained by shipment to and
filtration in the laboratory, the sample must be filtered in a designated clean area in the field within the time period necessary to maintain sample
integrity. A sample that has been collected for determination of total or dissolved trace level mercury must be analyzed within 90 days of sample
collection.
18 Aqueous samples must be preserved at ≤6 °C, and should not be frozen unless data demonstrating that sample freezing does not adversely
impact sample integrity is maintained on file and accepted as valid by the regulatory authority. Also, for purposes of NPDES monitoring, the
specification of ‘‘≤°C’’ is used in place of the ‘‘4 °C’’ and ‘‘< 4 °C’’ sample temperature requirements listed in some methods. It is not necessary
to measure the sample temperature to three significant figures (1⁄100th of 1 degree); rather, three significant figures are specified so that rounding
down to 6 °C may not be used to meet the ≤6 °C requirement. The preservation temperature does not apply to samples that are analyzed immediately (less than 15 minutes).
19 An aqueous sample may be collected and shipped without acid preservation. However, acid must be added at least 24 hours before analysis to dissolve any metals that adsorb to the container walls. If the sample must be analyzed within 24 hours of collection, add the acid immediately (see footnote 2). Soil and sediment samples do not need to be preserved with acid. The allowances in this footnote supersede the preservation and holding time requirements in the approved metals methods.
20 To achieve the 28-day holding time, use the ammonium sulfate buffer solution specified in EPA Method 218.6. The allowance in this footnote supersedes preservation and holding time requirements in the approved hexavalent chromium methods, unless this supersession would
compromise the measurement, in which case requirements in the method must be followed.
21 Holding time is calculated from time of sample collection to elution for samples shipped to the laboratory in bulk and calculated from the time
of sample filtration to elution for samples filtered in the field.
22 Samples analysis should begin immediately, preferably within 2 hours of collection. The maximum transport time to the laboratory is 6 hours,
and samples should be processed within 2 hours of receipt at the laboratory.
23 For fecal coliform samples for sewage sludge (biosolids) only, the holding time is extended to 24 hours for the following sample types using
either EPA Method 1680 (LTB–EC) or 1681 (A–1): Class A composted, Class B aerobically digested, and Class B anaerobically digested.
§ 503.8
PART 503—STANDARDS FOR THE
USE OR DISPOSAL OF SEWAGE
SLUDGE
3. The authority citation for Part 503
continues to read as follows:
I
cprice-sewell on PROD1PC66 with RULES2
Authority: Secs. 405(d) and (e) of the Clean
Water Act, as amended by Pub. L. 95–217,
sec. 54(d), 91 Stat. 1591 (33 U.S.C. 1345(d)
and (e)); and Pub. L. 100–4, title IV, sec.
406(a), (b), 101 Stat., 71, 72 (33 U.S.C. 1251
et seq.).
4. Section 503.8 is amended by
revising paragraph (b) introductory text
to read as follows:
I
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*
*
*
*
*
(b) Methods. The materials listed
below are incorporated by reference in
this part. These incorporations by
reference were approved by the Director
of the Federal Register in accordance
with 5 U.S.C. 552(a) and 1 CFR part 51.
The materials are incorporated as they
exist on the date of approval, and notice
of any change in these materials will be
published in the Federal Register. They
are available for inspection at the HQ
Water Docket Center, EPA/DC, EPA
West, Room B102, 1301 Constitution
Ave., NW., Washington, DC, and at the
National Archives and Records
PO 00000
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Administration (NARA). For
information on the availability of this
material at NARA, call 202–741–6030,
or go to: https://www.archives.gov/
federal_register/
code_of_federal_regulations/
ibr_locations.html.
Copies may be obtained from the
standard producer or publisher listed in
the regulation. The methods in the
materials listed below (or in 40 CFR Part
136) shall be used to analyze samples of
sewage sludge.
*
*
*
*
*
[FR Doc. 07–1455 Filed 3–23–07; 8:45 am]
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[Federal Register Volume 72, Number 57 (Monday, March 26, 2007)]
[Rules and Regulations]
[Pages 14220-14233]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 07-1455]
[[Page 14219]]
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Part III
Environmental Protection Agency
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40 CFR Parts 136 and 503
Guidelines Establishing Test Procedures for the Analysis of Pollutants;
Analytical Methods for Biological Pollutants in Wastewater and Sewage
Sludge; Final Rule
Federal Register / Vol. 72, No. 57 / Monday, March 26, 2007 / Rules
and Regulations
[[Page 14220]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 136 and 503
[EPA-HQ-OW-2004-0014; FRL-8228-1]
RIN 2040-AE68
Guidelines Establishing Test Procedures for the Analysis of
Pollutants; Analytical Methods for Biological Pollutants in Wastewater
and Sewage Sludge: Final Rule
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This rule modifies the EPA's Guidelines that establish
approved bacterial testing procedures for analysis and sampling under
the Clean Water Act. EPA proposed these changes for public comment on
August 16, 2005 and April 10, 2006. These changes include approval for
new methods for monitoring microbial pollutants in wastewater and
sewage sludge, including EPA methods, vendor-developed methods and
methods developed by voluntary consensus bodies (VCSB) as well as
updated versions of currently approved methods. The addition of new and
updated methods to the wastewater regulations provides increased
flexibility to the regulated community and laboratories in the
selection of analytical methods. In addition, EPA has made a technical,
non-substantive correction.
DATES: This regulation is effective April 25, 2007. The incorporation
by reference of these methods is approved by the Director of the
Federal Register on April 25, 2007. For judicial review purposes, this
final rule is promulgated as of 1 p.m. (Eastern time) on April 9, 2007
as provided at 40 CFR 23.2 and 23.7.
ADDRESSES: EPA has established a docket for this action under Docket ID
No. EPA-OW-2004-0014. All documents in the docket are listed on the
www.regulations.gov Web site. Although listed in the index, some
information is not publicly available, e.g., CBI or other information
whose disclosure is restricted by statute. Certain other material, such
as copyrighted material, is not placed on the Internet and will be
publicly available only in hard copy form. Publicly available docket
materials are available either electronically through
www.regulations.gov or in hard copy at the HQ Water Docket Center, EPA/
DC, EPA West, Room B102, 1301 Constitution Ave., NW., Washington, DC.
The Public Reading Room is open from 8:30 a.m. to 4:30 p.m., Monday
through Friday, excluding legal holidays. The telephone number for the
Public Reading Room is (202) 566-1744, and the telephone number is
(202) 566-2426.
Note: The EPA Docket Center suffered damage due to flooding
during the last week of June 2006. The Docket Center is continuing
to operate. However, during the cleanup, there will be temporary
changes to Docket Center telephone numbers, addresses, and hours of
operation for people who wish to visit the Public Reading Room to
view documents. Consult EPA's Federal Register notice at 71 FR 38147
(July 5, 2006) or the EPA website at https://www.epa.gov/epahome/
dockets.htm for current information on docket status, locations and
telephone numbers.
FOR FURTHER INFORMATION CONTACT: For information regarding the changes
to wastewater regulations, contact Robin K. Oshiro, Engineering and
Analysis Division (4303T), USEPA Office of Science and Technology, 1200
Pennsylvania Ave., NW., Washington, DC 20460, 202-566-1075 (e-mail:
oshiro.robin@epa.gov).
SUPPLEMENTARY INFORMATION:
A. Potentially Regulated Entities
1. Clean Water Act
EPA Regions, as well as States, Territories and Tribes authorized
to implement the National Pollutant Discharge Elimination System
(NPDES) program, issue permits with conditions designed to ensure
compliance with the technology-based and water quality-based
requirements of the Clean Water Act (CWA). These permits may include
restrictions on the quantity of pollutants that may be discharged as
well as pollutant measurement and reporting requirements. If EPA has
approved test procedures for analysis of a specific pollutant, an NPDES
permittee (or applicant for an NPDES permit) must use an approved test
procedure (or an approved alternate test procedure) for the specific
pollutant when testing for the required waste constituent. Similarly,
if EPA has established permit monitoring requirements, measurements
taken and reported under an NPDES permit must comply with these
requirements. Therefore, entities with NPDES permits will potentially
be regulated by the actions in this rulemaking. Categories and entities
that may potentially be subject to the requirements of today's rule
include:
------------------------------------------------------------------------
Examples of potentially
Category regulated entities
------------------------------------------------------------------------
State, Territorial, and Indian Tribal States, Territories, and Tribes
Governments. authorized to administer the
NPDES permitting program;
States, Territories, and
Tribes providing certification
under Clean Water Act section
401.
Industry............................... Facilities that must conduct
monitoring to comply with
NPDES permits.
Municipalities......................... POTWs that must conduct
monitoring to comply with
NPDES permits.
------------------------------------------------------------------------
This table is not intended to be exhaustive, but rather provides a
guide for readers regarding entities likely to be regulated by this
action. This table lists types of entities that EPA is now aware could
potentially be regulated by this action. Other types of entities not
listed in the table could also be regulated. To determine whether your
facility is regulated by this action, you should carefully examine the
applicability language at 40 CFR 122.1 (NPDES purpose and scope), 40
CFR 136.1 (NPDES permits and CWA), 40 CFR 403.1 (Pretreatment standards
purpose and applicability). If you have questions regarding the
applicability of this action to a particular entity, consult the
appropriate person listed in the preceding FOR FURTHER INFORMATION
CONTACT section.
What process governs judicial review of this rule?
Under Section 509(b)(1) of the Clean Water Act (CWA), judicial
review of today's CWA rule may be obtained by filing a petition for
review in the United States Circuit Court of Appeals within 120 days
from the date of promulgation of this rule. For judicial review
purposes, this final rule is promulgated as of 1 p.m. (Eastern time) on
April 25, 2007 as provided at 40 CFR 23.2. The requirements of this
regulation may also not be challenged later in civil or criminal
proceedings brought by EPA.
Abbreviations and Acronyms Used in the Preamble and Final Rule
AOAC: Association of Official Analytical Chemists International
ASTM: American Society for Testing and Materials International
[[Page 14221]]
CWA: Clean Water Act
EPA: Environmental Protection Agency
VCSB: Voluntary Consensus Standard Body
Table of Contents
I. Statutory Authority
Clean Water Act
II. Summary of Final Rule
A. 40 CFR Part 136
B. 40 CFR Part 503
III. Changes Between the Proposed Rule and the Final Rule
A. Revision to 40 CFR Part 136, Applicability
B. Revision to 40 CFR Part 136, Identification of Test
Procedures
C. Revision to 40 CFR Part 136, Table IA Title
D. Revisions to 40 CFR Part 136, Table II and Footnotes
E. Revisions to 40 CFR Part 503, Sampling and Analysis
IV. Response to Comments
Lack of Connecting Language Between 40 CFR Parts 136 and 503 for
Sewage Sludge Methods
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
B. Paperwork Reduction Act
C. Regulatory Flexibility Act
D. Unfunded Mandates Reform Act
E. Executive Order 13132: Federalism
F. Executive Order 13175: Consultation and Coordination with
Indian Tribal Governments
G. Executive Order 13045: Protection of Children from
Environmental Health Risks and Safety Risks
H. Executive Order 13211: Actions that Significantly Affect
Energy Supply, Distribution, or Use
I. National Technology Transfer and Advancement Act
J. Congressional Review Act
I. Statutory Authority
Clean Water Act
EPA is promulgating today's rule pursuant to the authority of
sections 301(a), 304(h), and 501(a) of the Clean Water Act (``CWA'' or
the ``Act''), 33 U.S.C. 1311(a), 1314(h), 1361(a). Section 301(a) of
the Act prohibits the discharge of any pollutant into navigable waters
unless the discharge complies with a National Pollutant Discharge
Elimination System (NPDES) permit issued under section 402 of the Act.
Section 304(h) of the Act requires the Administrator of the EPA to ``*
* * promulgate guidelines establishing test procedures for the analysis
of pollutants that shall include the factors which must be provided in
any certification pursuant to [section 401 of this Act] or permit
application pursuant to [section 402 of this Act].'' Section 501(a) of
the Act authorizes the Administrator to ``* * * prescribe such
regulations as are necessary to carry out this function under [the
Act].'' EPA generally has codified its test procedure regulations
(including analysis and sampling requirements) for CWA programs at 40
CFR Part 136, though some requirements are codified in other Parts
(e.g., 40 CFR Chapter I, Subchapters N and O).
II. Summary of Final Rule
The following sections describe the changes EPA is making in
today's final rule.
A. 40 CFR Part 136
This rule approves new and revised methods for inclusion in 40 CFR
Part 136. These methods include EPA methods, vendor methods submitted
by IDEXX and Hach, and voluntary consensus standards.
The following discussion briefly describes the changes to Part 136
methods approved today.
1. This rule amends the regulations at 40 CFR Part 136 to approve
five E. coli and two enterococci methods for monitoring microbial
pollutants in wastewaters. The E. coli methods include EPA Method 1603
(modified mTEC), and vendor methods Colilert[supreg] and Colilert-
18[supreg], and mColiBlue24[supreg]. The enterococci methods include
EPA Method 1600 (mEI), and vendor method EnterolertTM.
2. The rule approves two fecal coliform and one Salmonella method
for monitoring microbial pollutants in sewage sludge (biosolids). The
fecal coliform methods include EPA Methods 1680 (LT-EC) and 1681 (A-1)
and the Salmonella Method 1682 (Modified MSRV). The methods approved
today are alternative methods to those currently prescribed for
measuring fecal coliform and salmonella in sewage sludge identified in
40 CFR Sec. 503.8(b).
3. The rule amends the regulations by moving the microbial methods
approved for use in ambient waters from Table IA to a new Table IH, and
adding Table IH to section 136.3(a).
4. The rule extends the holding time for fecal coliforms using EPA
Methods 1680 (LTB-EC) or 1681 (A-1) in sewage sludge for Class A
composted, Class B aerobically or anaerobically digested sewage sludge.
5. The rule amends 40 CFR 136.1 to add a new provision that
authorizes the use of the methods identified at 40 CFR 503.8(b) and the
newly approved Part 136 methods for fecal coliform and Salmonella for
permit applications and recordkeeping and reporting required under
EPA's sewage sludge regulations at 40 CFR Part 503.
B. 40 CFR Part 503
This rule amends the regulations at 40 CFR Part 503 by adding a
cross reference to the 40 CFR Part 136 methods in section 503.8(b).
III. Changes Between the Proposed Rule and the Final Rule
Except as noted below, the content of the final rule is the same as
that of the proposed rule. In some instances, EPA revised for clarity
the language of the final rule from that in the proposed rule.
A. Revision to 40 CFR Part 136, Applicability
Based on comment received on the Agency's proposal of methods for
use in sewage sludge, EPA has amended the applicability provision to
clarify that the applicable procedures of Part 136 and Part 503 must be
used for measurements for sewage sludge permit applications and
reporting and recordkeeping requirements under Part 503.
B. Revision to 40 CFR Part 136, Identification of Test Procedures
Section 553 of the Administrative Procedure Act, 5 U.S.C.
553(b)(B), provides that, when an agency for good cause finds that
notice and public procedure are impracticable, unnecessary or contrary
to the public interest, the agency may issue a rule without providing
notice and an opportunity for public comment. EPA has determined that
there is good cause for making today's changes to the rule final
without prior proposal and opportunity for comment. Notice and
opportunity for public comment is not necessary with respect to these
changes because they are not substantive and merely correct errors in
cross-referenced provisions as explained below.
Section 136.3(a) provides that discharge parameter values for which
reports are required must be determined either by the standard
analytical test procedures described in the tables in Part 136 or
approved additional or alternate test procedures. EPA has modified the
language of 40 CFR 136.3(a) to make three corrections. First, EPA has
changed the citation in the last sentence before Table IA from
``paragraphs (b) or (c) of this section or 40 CFR 401.13'' to
``paragraphs (c) of this section, 40 CFR 136.5(a)-(d) and 40 CFR
401.13.'' Paragraph (b) does not describe circumstances in which
alternate procedures may be approved while section 136.5 does.
Second, EPA has deleted the clause at the end of the last sentence
which states that other test procedures may be used
``* * * when such other test procedures have been previously
approved by the Regional Administrator of the Region in which the
discharge will occur, and providing the Director of the State in
which
[[Page 14222]]
the discharge will occur does not object to the use of such
alternate test procedure * * *.''
Only two of the cited provisions require approval by the Regional
Administrator or Director of a State. 40 CFR 401.13 does not because it
pertains to variances of guidelines of national applicability.
The cross-referenced provisions authorize the use of additional or
alternate test procedures in described circumstances. Thus, section
136.3(c) authorizes approval by the Regional Administrator (or Director
of an approved State NPDES Program) for analysis of additional
pollutants or parameters required to be reported for a particular
discharge. Section 136.5(a)-(d) authorizes approval by the Regional
Administrator of alternate procedures for use within a particular EPA
Region. 40 CFR section 401.13 authorizes the use of analytical
procedures that are specifically defined in 40 CFR Parts 402-699. This
last category of analytical procedures that are promulgated for
specific effluent limitations guidelines and pretreatment standards and
not codified in Part 136 do not require the approval of the Director of
a State as the current language erroneously implies.
Third, EPA removed an erroneous reference that was listed as a
source for the methods listed in section 136.3.
EPA has modified the regulation to provide the correct citation and
delete the inaccurate and misleading language. None of the changes EPA
is promulgating today are themselves substantive but rather, as noted,
only either correct an error in citing to the other applicable
provisions of these regulations or correct inaccuracies. The
substantive provisions in question were previously subject to notice
and comment. Thus, notice and public procedures are unnecessary. EPA
finds that this constitutes good cause under 5 U.S.C. 553(b)(B).
C. Revision to 40 CFR Part 136, Table IA Title
The rule revises the title to Table IA from ``List of Approved
Biological Methods'' to ``List of Approved Biological Methods for
Wastewater and Sewage Sludge.'' Today's action updating Table IA at
Sec. 136.3 more clearly defines the removal of approved
microbiological methods for ambient waters from this table. Such
methods have been moved to a new table, Table IH.
D. Revisions to 40 CFR Part 136, Table II and Footnotes
The rule revises Table II (Required Containers, Preservation
Techniques, and Holding Times), and the footnotes to Table II at 40 CFR
136.3(e). Today's action updating Table II at Sec. 136.3(e) more
clearly defines the holding time for bacterial testing as 6 hours
holding time with 2 hours to process samples.
E. Revision to 40 CFR Part 503, Sampling and Analysis
Based on comments received on the Agency's proposal of methods for
use in sewage sludge, EPA is including a cross reference to 40 CFR Part
136 in 40 CFR 503.8(b) which prescribes the methods that must be used
for sampling and analysis of sewage sludge.
IV. Response to Comments
EPA received 39 comments regarding methods included in this final
rule from the August 16, 2005 proposal (70 FR 48256), and 9 comments on
the April 10, 2006 Notice of Data Availability (NODA) (71 FR 18329).
Commentors represented a number of different interests, including
analytical laboratories, water utilities, instrument manufacturers,
State and local governments, trade associations, scientists, and
private citizens. The public docket for this rule includes the Agency's
response to all comments. The majority of the comments were with regard
to method inclusion, method use, and quality control requirements. The
following is a summary of our response to comments about the lack of
connecting language between 40 CFR Parts 136 and 503 for sewage sludge
methods.
EPA proposed to approve methods in 40 CFR Part 136 for sewage
sludge but did not include an appropriate cross reference in 40 CFR
Part 503 to Part 136 so as to allow the use of appropriate 40 CFR 136.3
methods as alternative methods to those listed in 40 CFR 503.8. Based
on comments to the proposal, EPA has amended the language in 40 CFR
503.8(b). In addition, as discussed above, EPA has also amended the
language in 40 CFR 136.1 regarding the applicability of the methods in
this section to 40 CFR Part 503.
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
This action is not a ``significant regulatory action'' under the
terms of Executive Order (EO) 12866 (58 FR 51735, October 4, 1993) and
is therefore not subject to review under the EO.
B. Paperwork Reduction Act
This action does not impose an information collection burden under
the provisions of the Paperwork Reduction Act, 44 U.S.C. 3501 et seq.
This rule does not impose any information collection, reporting, or
recordkeeping requirements. This rule merely adds new and updated
versions of testing procedures, withdraws some older testing
procedures, and establishes new sample collection, preservation, and
holding time requirements.
Burden means the total time, effort, or financial resources
expended by persons to generate, maintain, retain, or disclose or
provide information to or for a Federal agency. This includes the time
needed to review instructions; develop, acquire, install, and utilize
technology and systems for the purpose of collecting, validating, and
verifying information, processing and maintaining information, and
disclosing and providing information; adjust the existing ways to
comply with any previously applicable instructions and requirements;
train personnel to be able to respond to a collection of information;
search data sources; complete and review the collection of information;
and transmit or otherwise disclose the information.
An Agency may not conduct or sponsor, and a person is not required
to respond to a collection of information unless it displays a
currently valid OMB control number. The OMB control numbers for EPA's
regulations in 40 CFR are listed in 40 CFR Part 9.
C. Regulatory Flexibility Act
The RFA generally requires an agency to prepare a regulatory
flexibility analysis of any rule subject to notice and comment
rulemaking requirements under the Administrative Procedure Act or any
other statute unless the agency certifies that the rule will not have a
significant economic impact on a substantial number of small entities.
Small entities include small businesses, small organizations, and small
governmental jurisdictions.
For purposes of assessing the impacts of this rule on small
entities for methods under the Clean Water Act, small entity is defined
as: (1) A small business as defined by the Small Business
Administration's (SBA) regulations at 13 CFR 121.201; (2) a small
governmental jurisdiction that is a government of a city, county, town,
school district or special district with a population less than 50,000;
and (3) a small organization that is any not-for-profit enterprise
which is independently owned and operated and is not dominant in its
field.
After considering the economic impacts of today's final rule on
small entities, I certify that this action will not have a significant
economic impact on a substantial number of small entities.
[[Page 14223]]
This final rule will not impose any requirements on small entities.
This action approves new and updated versions of testing procedures,
withdraws some older testing procedures, and approves new sample
collection, preservation, and holding time requirements. Generally,
these changes will have a positive impact on small entities by
increasing method flexibility, thereby allowing entities to reduce
costs by choosing more cost-effective methods. In some cases,
analytical costs may increase slightly due to the additional QC
requirements included in the methods that are being approved. However,
most laboratories that analyze samples for EPA compliance monitoring
have already instituted QC requirements as part of their laboratory
practices.
D. Unfunded Mandates Reform Act
Title II of the Unfunded Mandates Reform Act of 1995 (UMRA), Public
Law 104-4, establishes requirements for Federal agencies to assess the
effects of their regulatory actions on State, Tribal, and local
governments and the private sector. Under section 202 of the UMRA, EPA
generally must prepare a written statement, including a cost-benefit
analysis, for proposed and final rules with ``Federal mandates'' that
may result in expenditures to State, local, and Tribal governments, in
the aggregate, or to the private sector, of $100 million or more in any
one year. Before promulgating an EPA rule for which a written statement
is needed, section 205 of the UMRA generally requires EPA to identify
and consider a reasonable number of regulatory alternatives and adopt
the least costly, most cost-effective or least burdensome alternative
that achieves the objectives of the rule. The provisions of section 205
do not apply when they are inconsistent with applicable law. Moreover,
section 205 allows EPA to adopt an alternative other than the least
costly, most cost-effective or least burdensome alternative if the
Administrator publishes with the final rule an explanation of why that
alternative was not adopted.
Before EPA establishes any regulatory requirements that may
significantly or uniquely affect small governments, including Tribal
governments, it must have developed under section 203 of the UMRA a
small government agency plan. The plan must provide for the
notification of potentially affected small governments, enabling
officials of affected small governments to have meaningful and timely
input in the development of EPA regulatory proposals with significant
Federal intergovernmental mandates, and informing, educating, and
advising small governments on compliance with the regulatory
requirements.
This rule contains no Federal mandates (under the regulatory
provisions of Title II of UMRA) for State, local, or Tribal governments
or the private sector. The rule imposes no enforceable duty on any
State, local, or Tribal governments or the private sector. In fact,
this rule should (on the whole) save money for governments and the
private sector by increasing method flexibility, and allowing these
entities to reduce monitoring costs by taking advantage of innovations.
Thus, today's rule is not subject to the requirements of Sections 202
and 205 of the UMRA.
EPA has determined that this rule contains no regulatory
requirements that might significantly or uniquely affect small
governments. Generally, this action will have a positive impact by
increasing method flexibility, thereby allowing method users to reduce
costs by choosing more cost effective methods. In some cases,
analytical costs may increase slightly due to changes in methods, but
these increases are neither significant nor unique to small
governments. This rule merely approves new and updated versions of
testing procedures, withdraws some older testing procedures, and
approves new sample collection, preservation, and holding time
requirements. Thus, today's rule is not subject to the requirements of
Section 203 of UMRA.
E. Executive Order 13132: Federalism
Executive Order 13132, entitled ``Federalism'' (64 FR 43255, August
10, 1999), requires EPA to develop an accountable process to ensure
``meaningful and timely input by State and local officials in the
development of regulatory policies that have federalism implications.''
``Policies that have federalism implications'' is defined in the
Executive Order to include regulations that have ``substantial direct
effects on the States, on the relationship between the national
government and the States, or on the distribution of power and
responsibilities among the various levels of government.''
This final rule does not have federalism implications. It will not
have substantial direct effects on the States, on the relationship
between the national government and the States, or on the distribution
of power and responsibilities among the various levels of government,
as specified in Executive Order 13132. This rule merely approves new
and updated versions of testing procedures, withdraws some older
testing procedures, and approves new sample collection, preservation,
and holding time requirements. The costs to State and local governments
will be minimal (in fact, governments may see a cost savings), and the
rule does not preempt State law. Thus, Executive Order 13132 does not
apply to this rule.
In the spirit of Executive Order 13132, and consistent with EPA
policy to promote communications between EPA and State and local
governments, EPA specifically solicited comment on the proposed rule
from State and local officials.
F. Executive Order 13175: Consultation and Coordination With Indian
Tribal Governments
Executive Order 13175, entitled ``Consultation and Coordination
with Indian Tribal Governments'' (65 FR 67249, November 9, 2000),
requires EPA to develop an accountable process to ensure ``meaningful
and timely input by tribal officials in the development of regulatory
policies that have tribal implications.''
This final rule does not have tribal implications, as specified in
Executive Order 13175. It will not have substantial direct effects on
Tribal governments, on the relationship between the Federal government
and Indian tribes, or on the distribution of power and responsibilities
between the Federal government and Indian tribes. This rule merely
approves new and updated versions of testing procedures, withdraws some
older testing procedures, and approves new sample collection,
preservation, and holding time requirements. The costs to Tribal
governments will be minimal (in fact, governments may see a cost
savings), and the rule does not preempt State law. Thus, Executive
Order 13175 does not apply to this rule.
G. Executive Order 13045: Protection of Children From Environmental
Health Risks and Safety Risks
Executive Order 13045: ``Protection of Children from Environmental
Health Risks and Safety Risks'' (62 FR 19885, April 23, 1997) applies
to any rule that: (1) Is determined to be ``economically significant''
as defined under Executive Order 12866, and (2) concerns an
environmental health or safety risk that EPA has reason to believe may
have a disproportionate effect on children. If the regulatory action
meets both criteria, the Agency must evaluate the environmental health
or safety effects of the planned rule on children, and explain why the
planned regulation is preferable to other potentially effective and
reasonably feasible alternatives
[[Page 14224]]
considered by the Agency. This final rule is not subject to the
Executive Order 13045 because it is not economically significant as
defined in Executive Order 12866. Further it does not concern an
environmental health or safety risk that EPA has reason to believe may
have a disproportionate effect on children. This action approves new
and updated versions of testing procedures, withdraws some older
testing procedures, and approves new sample collection, preservation,
and holding time requirements.
H. Executive Order 13211: Actions That Significantly Affect Energy
Supply, Distribution, or Use
This rule is not subject to Executive Order 13211, ``Actions
Concerning Regulations That Significantly Affect Energy Supply,
Distribution, or Use'' (66 FR 28355 (May 22, 2001)) because it is not a
significant regulatory action under Executive Order 12866.
I. National Technology Transfer and Advancement Act
As noted in the proposed rule, Section 12(d) of the National
Technology Transfer and Advancement Act of 1995, (NTTAA), Public Law
104-113, section 12(d) (15 U.S.C. 272 note), directs EPA to use
voluntary consensus standards in its regulatory activities unless to do
so would be inconsistent with applicable law or otherwise impractical.
Voluntary consensus standards are technical standards (e.g., material
specifications, test methods, sampling procedures, and business
practices) that are developed or adopted by voluntary consensus
standard bodies. The NTTAA directs EPA to provide Congress, through the
OMB, explanations when the Agency decides not to use available and
applicable voluntary consensus standards. This rulemaking involves
technical standards. EPA has decided to use E. coli, enterococci and
fecal coliform methods published in Standard Methods and ASTM
International.
The E. coli methods from Standard Methods are method 9223B
(Standard Methods 18th, 19th and 20th Editions) and method 9223 B-97
(Standard Methods Online Edition), as well as AOAC method 991.15. The
enterococci method from ASTM is method D6503-99. The fecal coliform
methods from Standard Methods are methods 9221 C E (Standard Methods
18th, 19th and 20th Editions) and method 9221 C E-99 (Standard Methods
Online Edition). Standard Methods can be obtained from American Public
Health Association, 1015 15th Street, NW., Washington DC 20005, AOAC
methods can be obtained from Association of Official Analytical
Chemists International, 481 North Frederick Avenue, Suite 500,
Gaithersburg, MD 20877-2417, and ASTM methods can be obtained from ASTM
International, 100 Barr Harbor Drive, West Conshohocken, PA 19428.
These newly approved procedures reflect improvements in science and
technology. EPA believes that the addition of these methods offer a
wider variety of options that may be more cost effective to conduct
compliance monitoring of bacterial pollutants.
J. Congressional Review Act
The Congressional Review Act, 5 U.S.C. 801 et seq., as added by the
Small Business Regulatory Enforcement Fairness Act of 1996, generally
provides that before a rule may take effect, the agency promulgating
the rule must submit a rule report, which includes a copy of the rule,
to each House of the Congress and to the Comptroller General of the
United States. EPA will submit a report containing this rule and other
required information to the U.S. Senate, the U.S. House of
Representatives, and the Comptroller General of the United States prior
to publication of the rule in the Federal Register. A major rule cannot
take effect until 60 days after it is published in the Federal
Register. This action is not a ``major rule'' as defined by 5 U.S.C.
804(2). This rule will be effective April 25, 2007.
List of Subjects
40 CFR Part 136
Environmental protection, Incorporation by reference, Reporting and
recordkeeping requirements, Water pollution control.
40 CFR Part 503
Environmental protection, Reporting and recordkeeping requirements,
Waste treatment and disposal, Water pollution control.
Dated: September 28, 2006.
Stephen L. Johnson,
Administrator.
Editorial Note: The Office of the Federal Register received this
document on March 8, 2007.
0
For the reasons set out in the preamble, title 40, chapter I of the
Code of Federal Regulations, is amended as follows:
PART 136--GUIDELINES ESTABLISHING TEST PROCEDURES FOR THE ANALYSIS
OF POLLUTANTS
0
1. The authority citation for Part 136 continues to read as follows:
Authority: Secs. 301, 304(h), 307, and 501(a) Pub. L. 95-217, 91
Stat. 1566, et seq. (33 U.S.C. 1251, et seq.) (The Federal Water
Pollution Control Act Amendments of 1972 as amended by the Clean
Water Act of 1977.)
0
2. Section 136.1 is revised to read as follows:
Sec. 136.1 Applicability.
(a) The procedures prescribed herein shall, except as noted in
Sec. 136.5, be used to perform the measurements indicated whenever the
waste constituent specified is required to be measured for:
(1) An application submitted to the Administrator, or to a State
having an approved NPDES program for a permit under section 402 of the
Clean Water Act of 1977, as amended (CWA), and/or to reports required
to be submitted under NPDES permits or other requests for quantitative
or qualitative effluent data under parts 122 to 125 of title 40, and,
(2) Reports required to be submitted by dischargers under the NPDES
established by parts 124 and 125 of this chapter, and,
(3) Certifications issued by States pursuant to section 401 of the
CWA, as amended.
(b) The procedure prescribed herein and in part 503 of title 40
shall be used to perform the measurements required for an application
submitted to the Administrator or to a State for a sewage sludge permit
under section 405(f) of the Clean Water Act and for recordkeeping and
reporting requirements under part 503 of title 40.
0
3. Section 136.3 is amended as follows:
0
a. By revising paragraph (a) introductory text and Table IA.
0
b. In paragraph (a) by adding Table IH after the notes of Table IG.
0
c. In paragraph (b) by revising the introductory text and by revising
references 2, 6, 10, 11, 34, 38, 39, and 52 through 62; and by adding
references 70 through 72.
0
d. By revising paragraph (e).
Sec. 136.3 Identification of test procedures.
(a) Parameters or pollutants, for which methods are approved, are
listed together with test procedure descriptions and references in
Tables IA, IB, IC, ID, IE, IF, IG, and IH. In the event of a conflict
between the reporting requirements of 40 CFR Parts 122 and 125 and any
reporting requirements associated with the methods listed in these
tables, the provisions of 40 CFR Parts 122 and 125 are controlling and
will determine a permittee's reporting requirements. The full text of
the referenced test procedures are incorporated by reference into
Tables
[[Page 14225]]
IA, IB, IC, ID, IE, IF, IG, and IH. The incorporation by reference of
these documents, as specified in paragraph (b) of this section, was
approved by the Director of the Federal Register in accordance with 5
U.S.C. 552(a) and 1 CFR Part 51. Copies of the documents may be
obtained from the sources listed in paragraph (b) of this section.
Documents may be inspected at EPA's Water Docket, EPA West, 1301
Constitution Avenue, NW., Room B102, Washington, DC (Telephone: 202-
566-2426); or at the National Archives and Records Administration
(NARA). For information on the availability of this material at NARA,
call 202-741-6030, or go to: https://www.archives.gov/federal_register/
code_of_federal_regulations/ibr_locations.html. These test
procedures are incorporated as they exist on the day of approval and a
notice of any change in these test procedures will be published in the
Federal Register. The discharge parameter values for which reports are
required must be determined by one of the standard analytical test
procedures incorporated by reference and described in Tables IA, IB,
IC, ID, IE, IF, IG, and IH or by any alternate test procedure which has
been approved by the Administrator under the provisions of paragraph
(d) of this section and Sec. Sec. 136.4 and 136.5. Under certain
circumstances paragraph (c) of this section, Sec. 136.5(a) through (d)
or 40 CFR 401.13, other additional or alternate test procedures may be
used.
Table IA.--List of Approved Biological Methods for Wastewater and Sewage Sludge
--------------------------------------------------------------------------------------------------------------------------------------------------------
Standard methods
Parameter and units Method \1\ EPA 18th, 19th, 20th Standard methods AOAC, ASTM, USGS Other
ed. online
--------------------------------------------------------------------------------------------------------------------------------------------------------
Bacteria:
1. Coliform (fecal), number Most Probable p. 132 \3\........ 9221 C E.......... 9221 C E-99.......
per 100 mL or number per Number (MPN),\5\ 1680 \12,14\......
gram dry weight. tube 3 dilution, 1681 \12,19\......
or
Membrane filter p. 124 \3\........ 9222 D............ 9222 D-97......... B-0050-85 \5\.....
(MF) \2\, single
step.
2. Coliform (fecal) in MPN, 5 tube, 3 p. 132 \3\........ 9221 C E.......... 9221 C E-99.......
presence of chlorine, dilution, or
number per 100 mL.
MF \2\, single p. 124 \3\........ 9222 D............ 9222 D-97.........
step.
3. Coliform (total), number MPN, 5 tube, 3 p. 114 \3\........ 9221 B............ 9221 B-99.........
per 100 mL. dilution, or
MF \2\, single p. 108 \3\........ 9222 B............ 9222 B-97......... B-0025-8 \5\......
step or two step.
4. Coliform (total), in MPN, 5 tube, 3 p. 114 \3\........ 9221 B............ 9221 B-99.........
presence of chlorine, dilution, or
number per 100 mL.
MF \2\ with p. 111 \3\........ 9222 (B+B.5c)..... 9222 (B+B.5c)-97..
enrichment.
5. E. coli, number per 100 MPN \7,9,15\ .................. 9223 B \13\....... 9223 B-97 \13\.... 991.15 \11\....... Colilert[supreg]\1
mL \20\. multiple tube/ 3,17\
multiple well. Colilert-
18[supreg]\13,16,
17\
MF \2,6,7,8,9\ 1603 \21\......... .................. .................. .................. mColiBlue-
single step. 24[supreg]\18\
6. Fecal streptococci, MPN, 5 tube 3 p. 139 \3\........ 9230 B............ 9230 B-93.........
number per 100 mL. dilution,.
MF \2\, or........ p. 136 \3\........ 9230 C............ 9230 C-93......... B-0055-85 \5\.....
Plate count....... p. 143 \3\........
7. Enterococci, number per MPN \7,9\, .................. .................. .................. D6503-99 \10\..... Enterolert[supreg]
100 mL \20\. multiple tube/ \13,23\
multiple well.
MF \2,6,7,8,9\ 1600 \24\.........
single step.
8. Salmonella, number per MPN multiple tube. 1682 \22\.........
gram dry weight \12\.
Aquatic Toxicity:
9. Toxicity, acute, fresh Ceriodaphnia dubia 2002.0 \25\.......
water organisms, LC 50, acute.
percent effluent.
Daphnia puplex and 2021.0 \25\.......
Daphnia magna
acute.
Fathead Minnow, 2000.0 \25\.......
Pimephales
promelas, and
Bannerfin shiner,
Cyprinella
leedsi, acute.
[[Page 14226]]
Rainbow Trout, 2019.0 \25\.......
Oncorhynchus
mykiss, and brook
trout, Salvelinus
fontinalis, acute.
10. Toxicity, acute, Mysid, Mysidopsis 2007.0 \25\.......
estuarine and marine bahia, acute.
organisms of the Atlantic
Ocean and Gulf of Mexico,
LC50, percent effluent.
Sheepshead Minnow, 2004.0 \25\.......
Cyprinodon
variegatus, acute.
Silverside, 2006.0 \25\.......
Menidia
beryllina,
Menidia menidia,
and Menidia
peninsulae, acute.
11. Toxicity, chronic, fresh Fathead minnow, 1000.0 \26\.......
water organisms, NOEC or Pimephales
IC25, percent effluent. promelas, larval
survival and
growth.
Fathead minnow, 1001.0 \26\.......
Pimephales
promelas, embryo-
larval survival
and
teratogenicity.
Daphnia, 1002.0 \26\.......
Ceriodaphnia
dubia, survival
and reproduction.
Green alga, 1003.0 \26\.......
Selenastrum
capricornutum,
growth.
12. Toxicity, chronic, Sheepshead minnow, 1004.0 \27\.......
estuarine and marine Cyprinodon
organisms of the Atlantic variegatus,
Ocean and Gulf of Mexico, larval survival
NOEC or IC25, percent and growth.
effluent.
Sheepshed minnow, 1005.0 \27\.......
Cyprinodon
variegatus,
embryo-larval
survival and
teratogenicity.
Inland silverside, 1006.0 \27\.......
Menidia
beryllina, larval
survival and
growth.
Mysid, Mysidopsis 1007.0 \27\.......
bahia, survival,
growth, and
fecundity.
Sea urchin, 1008.0 \27\.......
Arbacia
punctulata,
fertilization.
--------------------------------------------------------------------------------------------------------------------------------------------------------
\1\ The method must be specified when results are reported.
\2\ A 0.45 [mu]m membrane filter (MF) or other pore size certified by the manufacturer to fully retain organisms to be cultivated and to be free of
extractables which could interfere with their growth.
\3\ USEPA. 1978. Microbiological Methods for Monitoring the Environment, Water, and Wastes. Environmental Monitoring and Support Laboratory, U.S.
Environmental Protection Agency, Cincinnati, OH, EPA/600/8-78/017.
\4\ [Reserved].
\5\ USGS. 1989. U.S. Geological Survey Techniques of Water-Resource Investigations, Book 5, Laboratory Analysis, Chapter A4, Methods for Collection and
Analysis of Aquatic Biological and Microbiological Samples, U.S. Geological Survey, U.S. Department of the Interior, Reston, VA.
\6\ Because the MF technique usually yields low and variable recovery from chlorinated wastewaters, the Most Probable Number method will be required to
resolve any controversies.
\7\ Tests must be conducted to provide organism enumeration (density). Select the appropriate configuration of tubes/filtrations and dilutions/volumes
to account for the quality, character, consistency, and anticipated organism density of the water sample.
[[Page 14227]]
\8\ When the MF method has been used previously to test waters with high turbidity, large numbers of noncoliform bacteria, or samples that may contain
organisms stressed by chlorine, a parallel test should be conducted with a multiple-tube technique to demonstrate applicability and comparability of
results.
\9\ To assess the comparability of results obtained with individual methods, it is suggested that side-by-side tests be conducted across seasons of the
year with the water samples routinely tested in accordance with the most current Standard Methods for the Examination of Water and Wastewater or EPA
alternate test procedure (ATP) guidelines.
\10\ ASTM. 2000, 1999, 1996. Annual Book of ASTM Standards--Water and Environmental Technology. Section 11.02. ASTM International. 100 Barr Harbor
Drive, West Conshohocken, PA 19428.
\11\ AOAC. 1995. Official Methods of Analysis of AOAC International, 16th Edition, Volume I, Chapter 17. Association of Official Analytical Chemists
International. 481 North Frederick Avenue, Suite 500, Gaithersburg, MD 20877-2417.
\12\ Recommended for enumeration of target organism in sewage sludge.
\13\ These tests are collectively known as defined enzyme substrate tests, where, for example, a substrate is used to detect the enzyme [beta]-
glucuronidase produced by E. coli.
\14\ USEPA. July 2006. Method 1680: Fecal Coliforms in Sewage Sludge (Biosolids) by Multiple-Tube Fermentation Using Lauryl-Tryptose Broth (LTB) and EC
Medium. US Environmental Protection Agency, Office of Water, Washington, DC EPA-821-R-06-012.
\15\ Samples shall be enumerated by the multiple-tube or multiple-well procedure. Using multiple-tube procedures, employ an appropriate tube and
dilution configuration of the sample as needed and report the Most Probable Number (MPN). Samples tested with Colilert[supreg] may be enumerated with
the multiple-well procedures, Quanti-Tray[supreg] Quanti-Tray[supreg] 2000, and the MPN calculated from the table provided by the manufacturer.
\16\ Colilert-18[supreg] is an optimized formulation of the Colilert[supreg] for the determination of total coliforms and E. coli that provides results
within 18 h of incubation at 35 [deg]C rather than the 24 h required for the Colilert[supreg] test and is recommended for marine water samples.
\17\ Descriptions of the Colilert[supreg], Colilert-18[supreg], Quanti-Tray[supreg], and Quanti-Tray[supreg]/2000 may be obtained from IDEXX
Laboratories, Inc., 1 IDEXX Drive, Westbrook, ME 04092.
\18\ A description of the mColiBlue24[supreg] test, Total Coliforms and E. coli, is available from Hach Company, 100 Dayton Ave., Ames, IA 50010.
\19\ USEPA. July 2006. Method 1681: Fecal Coliforms in Sewage Sludge (Biosolids) by Multiple-Tube Fermentation using A-1 Medium. U.S. Environmental
Protection Agency, Office of Water, Washington, DC EPA-821-R-06-013.
\20\ Recommended for enumeration of target organism in wastewater effluent.
\21\ USEPA. July 2006. Method 1603: Escherichia coli (E. coli) in Water by Membrane Filtration Using Modified membrane-Thermotolerant Escherichia coli
Agar (modified mTEC). U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA-821-R-06-011.
\22\ USEPA. July 2006. Method 1682: Salmonella in Sewage Sludge (Biosolids) by Modified Semisolid Rappaport-Vassiliadis (MSRV) Medium. U.S.
Environmental Protection Agency, Office of Water, Washington, DC EPA-821-R-06-014.
\23\ A description of the Enterolert[supreg] test may be obtained from IDEXX Laboratories, Inc., 1 IDEXX Drive, Westbrook, ME 04092.
\24\ USEPA. July 2006. Method 1600: Enterococci in Water by Membrane Filtration Using membrane-Enterococcus Indoxyl-[beta]-D-Glucoside Agar (mEI). U.S.
Environmental Protection Agency, Office of Water, Washington, DC EPA-821-R-06-009.
\25\ USEPA. October 2002. Methods for Measuring the Acute Toxicity of Effluents and Receiving Waters to Freshwater and Marine Organisms. Fifth Edition.
U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA/821/R-02/012.
\26\ USEPA. October 2002. Short-term Methods for Estimating the Chronic Toxicity of Effluents and Receiving Waters to Freshwater Organisms. Fourth
Edition, U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA/821/R-02/013.
\27\ USEPA. October 2002. Short-term Methods for Estimating the Chronic Toxicity of Effluents and Receiving Waters to Marine and Estuarine Organisms.
Third Edition. U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA/821/R-02/014.
* * * * *
Table IH.--List of Approved Microbiological Methods for Ambient Water
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Standard methods
Parameter and units Method \1\ EPA 18th, 19th, 20th Standard methods AOAC, ASTM, USGS Other
Ed. online
--------------------------------------------------------------------------------------------------------------------------------------------------------
Bacteria:
1. E. coli, number per 100 MPN \6,8,14\ .................. 9221 B.1/9221 F 9221 B.1-99/9221 F
mL. multiple tube, \11,13\. \11,13\.
Multiple tube/ .................. 9223 B \12\....... 9223 B-97 \12\.... 991.15 \10\....... Colilert[supreg]
multiple well, \12,16\ Colilert-
18[supreg]
\12,15,16\.
MF \2,5,6,7,8\ two 1103.1 \19\....... 9222 B/9222 G 9222 B-97/9222 G D5392-93 \9\......
step, or \18\, 9213 D. \18\.
Single step....... 1603 \20\, 1604 .................. .................. .................. mColiBlue-
\21\. 24[supreg] \17\.
2. Enterococci, number per MPN \6,8\ multiple .................. 9230 B............ 9230 B-93.........
100 mL. tube,
Multiple tube/ .................. .................. .................. D6503-99 \9\...... Enterolert[supreg]
multiple well. \12,22\.
MF \2,5,6,7,8\ two 1106.1 \23\....... 9230 C............ 9230 C-93......... D5259-92 \9\......
step.
Single step, or... 1600 \24\.........
Plate count....... p. 143 \3\........
Protozoa:
3. Cryptosporidium.......... Filtration/IMS/FA. 1622 \25,\1623
\26\.
4. Giardia.................. Filtration/IMS/FA. 1623 \26\.........
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\1\ The method must be specified when results are reported.
\2\ A 0.45 [mu]m membrane filter (MF) or other pore size certified by the manufacturer to fully retain organisms to be cultivated and to be free of
extractables which could interfere with their growth.
\3\ USEPA. 1978. Microbiological Methods for Monitoring the Environment, Water, and Wastes. Environmental Monitoring and Support Laboratory, U.S.
Environmental Protection Agency, Cincinnati, OH. EPA/600/8-78/017.
\4\ [Reserved]
\5\ Because the MF technique usually yields low and variable recovery from chlorinated wastewaters, the Most Probable Number method will be required to
resolve any controversies.
\6\ Tests must be conducted to provide organism enumeration (density). Select the appropriate configuration of tubes/filtrations and dilutions/volumes
to account for the quality, character, consistency, and anticipated organism density of the water sample.
[[Page 14228]]
\7\ When the MF method has not been used previously to test waters with high turbidity, large number of noncoliform bacteria, or samples that may
contain organisms stressed by chlorine, a parallel test should be conducted with a multiple-tube technique to demonstrate applicability and
comparability of results.
\8\ To assess the comparability of results obtained with individual methods, it is suggested that side-by-side tests be conducted across seasons of the
year with the water samples routinely tested in accordance with the most current Standard Methods for the Examination of Water and Wastewater or EPA
alternate test procedure (ATP) guidelines.
\9\ ASTM. 2000, 1999, 1996. Annual Book of ASTM Standards--Water and Environmental Technology. Section 11.02. ASTM International. 100 Barr Harbor Drive,
West Conshohocken, PA 19428.
\10\ AOAC. 1995. Official Methods of Analysis of AOAC International, 16th Edition, Volume I, Chapter 17. Association of Official Analytical Chemists
International. 481 North Frederick Avenue, Suite 500, Gaithersburg, MD 20877-2417.
\11\ The multiple-tube fermentation test is used in 9221B.1. Lactose broth may be used in lieu of lauryl tryptose broth (LTB), if at least 25 parallel
tests are conducted between this broth and LTB using the water samples normally tested, and this comparison demonstrates that the false-positive rate
and false-negative rate for total coliform using lactose broth is less than 10 percent. No requirement exists to run the completed phase on 10 percent
of all total coliform-positive tubes on a seasonal basis.
\12\ These tests are collectively known as defined enzyme substrate tests, where, for example, a substrate is used to detect the enzyme [beta]-
glucuronidase produced by E. coli.
\13\ After prior enrichment in a presumptive medium for total coliform using 9221B.1, all presumptive tubes or bottles showing any amount of gas, growth
or acidity within 48 h 3 h of incubation shall be submitted to 9221F. Commercially available EC-MUG media or EC media supplemented in the
laboratory with 50 [mu]g/mL of MUG may be used.
\14\ Samples shall be enumerated by the multiple-tube or multiple-well procedure. Using multiple-tube procedures, employ an appropriate tube and
dilution configuration of the sample as needed and report the Most Probable Number (MPN). Samples tested with Colilert[supreg] may be enumerated with
the multiple-well procedures, Quanti-Tray[supreg] or Quanti-Tray[supreg] 2000, and the MPN calculated from the table provided by the manufacturer.
\15\ Colilert-18[supreg] is an optimized formulation of the Colilert[supreg] for the determination of total coliforms and E. coli that provides results
within 18 h of incubation at 35 [deg]C rather than the 24 h required for the Colilert[supreg] test and is recommended for marine water samples.
\16\ Descriptions of the Colilert[supreg], Colilert-18[supreg], Quanti-Tray[supreg], and Quanti-Tray[supreg]/2000 may be obtained from IDEXX
Laboratories, Inc., 1 IDEXX Drive, Westbrook, ME 04092.
\17\ A description of the mColiBlue24[supreg] test, Total Coliforms and E. coli, is available from Hach Company, 100 Dayton Ave., Ames, IA 50010.
\18\ Subject total coliform positive samples determined by 9222B or other membrane filter procedure to 9222G using NA-MUG media.
\19\ USEPA. July 2006. Method 1103.1: Escherichia coli (E. coli) in Water by Membrane Filtration Using membrane-Thermotolerant Escherichia coli Agar
(mTEC). U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA-821-R-06-010.
\20\ USEPA. July 2006. Method 1603: Escherichia coli (E. coli) in Water by Membrane Filtration Using Modified membrane-Thermotolerant Escherichia coli
Agar (Modified mTEC). U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA-821-R-06-011.
\21\ Preparation and use of MI agar with a standard membrane filter procedure is set forth in the article, Brenner et al. 1993. ``New Medium for the
Simultaneous Detection of Total Coliform and Escherichia coli in Water.'' Appl. Environ. Microbiol. 59:3534-3544 and in USEPA. September 2002.: Method
1604: Total Coliforms and Escherichia coli (E. coli) in Water by Membrane Filtration by Using a Simultaneous Detection Technique (MI Medium). U.S.
Environmental Protection Agency, Office of Water, Washington, DC EPA 821-R-02-024.
\22\ A description of the Enterolert[supreg] test may be obtained from IDEXX Laboratories, Inc., 1 IDEXX Drive, Westbrook, ME 04092.
\23\ USEPA. July 2006. Method 1106.1: Enterococci in Water by Membrane Filtration Using membrane-Enterococcus-Esculin Iron Agar (mE-EIA). U.S.
Environmental Protection Agency, Office of Water, Washington, DC EPA-821-R-06-008.
\24\ USEPA. July 2006. Method 1600: Enterococci in Water by Membrane Filtration Using membrane-Enterococcus Indoxyl-[beta]-D-Glucoside Agar (mEI). U.S.
Environmental Protection Agency, Office of Water, Washington, DC EPA-821-R-06-009.
\25\ Method 1622 uses filtration, concentration, immunomagnetic separation of oocysts from captured material, immunofluorescence assay to determine
concentrations, and confirmation through vital dye staining and differential interference contrast microscopy for the detection of Cryptosporidium.
USEPA. 2001. Method 1622: Cryptosporidium in Water by Filtration/IMS/FA. U.S. Environmental Protection Agency, Office of Water, Washington, DC EPA-821-
R-01-026.
\26\ Method 1623 uses filtration, concentration, immunomagnetic separation of oocysts and cysts from captured material, immunofluorescence assay to
determine concentrations, and confirmation through vital dye staining and differential interference contrast microscopy for the simultaneous detection
of Cryptosporidium and Giardia oocysts and cysts. USEPA. 2001. Method 1623. Cryptosporidium and Giardia in Water by Filtration/IMS/FA. U.S.
Environmental Protection Agency, Office of Water, Washington, DC EPA-821-R-01-025.
(b) The full texts of the methods from the following references
which are cited in Tables IA, IB, IC, ID, IE, IF, IG and IH are
incorporated by reference into this regulation and may be obtained from
the source identified. All costs cited are subject to change and must
be verified from the indicated source. The full texts of all the test
procedures cited are available for inspection at the National Archives
and Records Administration (NARA). For information on the availability
of this material at NARA, call 202-741-6030, or go to: https://
www.archives.gov/federal_register/code_of_federal_regulations/ibr_
locations.html.
References, Sources, Costs, and Table Citations
* * * * *
(2) USEPA. 1978. Microbiological Methods for Monitoring the
Environment, Water, and Wastes. Environmental Monitoring and Support
Laboratory, U.S. Environmental Protection Agency, Cincinnati, Ohio.
EPA/600/8-78/017. Available at https://www.epa.gov/clariton/srch.htm or
from: National Technical Information Service, 5285 Port Royal Road,
Springfield, Virginia 22161, Pub. No. PB-290329/A.S. Table IA, Note 3;
Table IH, Note 3.
* * * * *
(6) American Public Health Association. 1992, 1995, and 1998.
Standard Methods for the Examination of Water and Wastewater. 18th,
19th, and 20th Edition (respectively). Available from: American Public
Health Association, 1015 15th Street, NW., Washington, DC 20005.
Standard Methods Online is available through the Standard Methods Web
site (https://www.standardmethods.org). Tables IA, IB, IC, ID, IE, and
IH.
* * * * *
(10) ASTM International. Annual Book of ASTM Standards, Water, and
Environmental Technology, Section 11, Volumes 11.01 and 11.02, 1994,
1996, 1999, Volume 11.02, 2000, and individual standards published
after 2000. Available from: ASTM International, 100 Barr Harbor Drive,
P.O. Box C700, West Conshohocken, PA 19428-2959, or https://
www.astm.org. Tables IA, IB, IC, ID, IE, and IH.
* * * * *
(11) USGS. 1989. U.S. Geological Survey Techniques of Water-
Resources Investigations, Book 5, Laboratory Analys