Guidelines Establishing Test Procedures for the Analysis of Pollutants Under the Clean Water Act; National Primary Drinking Water Regulations; and National Secondary Drinking Water Regulations; Analysis and Sampling Procedures, 11200-11249 [07-1073]
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Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Parts 122, 136, 141, 143, 430,
455, and 465
[EPA–HQ–OW–2003–0070; FRL–8203–8]
RIN 2040–AD71
Guidelines Establishing Test
Procedures for the Analysis of
Pollutants Under the Clean Water Act;
National Primary Drinking Water
Regulations; and National Secondary
Drinking Water Regulations; Analysis
and Sampling Procedures
Environmental Protection
Agency (EPA).
ACTION: Final rule.
AGENCY:
SUMMARY: This rule modifies the testing
procedures approved for analysis and
sampling under the Clean Water Act
and Safe Drinking Water Act. EPA
proposed these changes for public
comment on August 18, 2003 and April
6, 2004. The Clean Water Act changes
adopted in this final rule fall into the
following categories: new vendordeveloped methods as well as EPA and
voluntary consensus standard bodies
(VCSB) methods, updated versions of
currently approved methods, revisions
to method modification and analytical
requirements, withdrawal of certain
outdated methods, and changes to
sample collection, preservation, and
holding time requirements. This rule
also changes regulations under the Safe
Drinking Water Act that establish
drinking water sampling and analysis
procedures. The changes include
approval of vendor-developed methods,
new EPA and VCSB methods, updated
VCSB methods, and approval of a
modification to the test kit used with
Syngenta Method AG–625 that restricts
its use in certain circumstances. The
addition of new and updated methods
to the wastewater and drinking water
regulations provides increased
flexibility to the regulated community
and laboratories in the selection of
analytical methods.
ADDRESSES: EPA has established a
docket for this action under Docket ID
No. EPA–OW–2003–0070. All
documents in the docket are listed on
the https://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
https://www.regulations.gov or in hard
copy at the HQ Water Docket Center,
EPA/DC, EPA West, Room 3334, 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 for the HQ Water Docket Center.
DATES: This regulation is effective April
11, 2007. The incorporation by reference
of these methods is approved by the
Director of the Federal Register on April
11, 2007. For judicial review purposes,
this final rule is promulgated as of 1:00
p.m. (Eastern time) on March 26, 2007
as provided at 40 CFR 23.2 and 23.7.
FOR FURTHER INFORMATION CONTACT: For
information regarding the changes to
wastewater regulations, contact Meghan
Hessenauer, Engineering and Analysis
Division (4303T), USEPA Office of
Science and Technology, 1200
Pennsylvania Ave., NW., Washington,
DC 20460, 202–566–1040 (e-mail:
hessenauer.meghan@epa.gov). For
information regarding the changes to
drinking water regulations, contact
Patricia Snyder Fair, Technical Support
Center (MS 140), USEPA, Office of
Ground Water and Drinking Water, 26
West Martin Luther King Drive,
Cincinnati, OH 45268, 513–569–7937 (email: fair.pat@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 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, the NPDES permittee must
use an approved test procedure (or an
approved alternate test procedure) for
the specific pollutant when measuring
the required waste constituent.
Similarly, if EPA has established
sampling requirements, measurements
taken 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 regulated entities
State, Territorial, and Indian Tribal
Governments.
Industry ...........................................
Municipalities ...................................
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Category
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.
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
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(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.
2. Safe Drinking Water Act
Public water systems are the regulated
entities required to measure
contaminants in drinking water
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samples. In addition, EPA Regions, as
well as States, and Tribal governments
with authority to administer the
regulatory program for public water
systems under the Safe Drinking Water
Act, may also measure contaminants in
water samples. When EPA establishes a
maximum contaminant level (MCL) for
a given drinking water contaminant, the
Agency also approves standardized test
procedures for analysis of the
contaminant. Public water systems
required to test water samples must use
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one of the approved test procedures.
Categories and entities that may
ultimately be subject to the
requirements of today’s rule include:
Category
Examples of potentially regulated entities
State, Local, & Tribal Governments ...........
States, local and tribal governments that analyze water samples on behalf of public
water systems required to conduct such analysis; States, local and tribal governments that themselves operate community and non-transient non-community water
systems required to monitor.
Private operators of community and non-transient non-community water systems required to monitor.
Municipal operators of community and non-transient non-community water systems
required to monitor.
Industry .......................................................
Municipalities ..............................................
1 North
NAICS 1
924110
221310
924110
American Industry Classification System.
This table is not intended to be
exhaustive, but rather provides a guide
for readers regarding entities likely to be
regulated by this action. The 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 141.2 (definition of
public water system). 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.
B. 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 March 26,
2007 as provided at 40 CFR 23.2. Under
section 1448 (a) of the Safe Drinking
Water Act (SDWA), judicial review of
today’s SDWA rule may be obtained by
filing a petition for review only in the
United States Court of Appeal for the
District of Columbia Circuit within 45
days from the date of promulgation of
this rule. For SDWA judicial review
purposes, this final rule is promulgated
as of 1 p.m. (Eastern time) on March 26,
2007 as provide at 40 CFR 23.7. The
requirements of this regulation may also
not be challenged later in civil or
criminal proceedings brought by EPA.
C. Abbreviations and Acronyms Used
in the Preamble and Final Rule
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AOAC: AOAC-International
ASTM: ASTM International
ATP: Alternate Test Procedure
CWA: Clean Water Act
EPA: Environmental Protection Agency
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FLAA: Flame Atomic Absorption
Spectroscopy
ICP–AES: Inductively Coupled PlasmaAtomic Emission Spectroscopy
ICP–MS: Inductively Coupled Plasma-Mass
Spectroscopy
NPDES: National Pollutant Discharge
Elimination System
NPDWR: National Primary Drinking Water
Regulations
NSDWR: National Secondary Drinking
Water Regulations
QC: Quality Control
SDWA: Safe Drinking Water Act
STGFAA: Stabilized Temperature Graphite
Furnace Atomic Absorption Spectroscopy
USGS: United States Geological Survey
VCSB: Voluntary Consensus Standard Body
D. Table of Contents
I. Statutory Authority
A. Clean Water Act
B. Safe Drinking Water Act
II. Summary of Final Rule
A. 40 CFR Part 122
B. 40 CFR Part 136
C. 40 CFR Parts 141 and 143
D. 40 CFR Part 430
E. 40 CFR Part 455
F. 40 CFR Part 465
III. Changes Between the Proposed Rule and
the Final Rule
A. Silver Determinations
B. ASTM Method D5673–02 ‘‘Standard
Test Method for Elements in Water by
Inductively Coupled Plasma—Mass
Spectrometry’’
C. Ammonia Determinations
D. Available Cyanide Determinations
E. Kelada-01 Method for Determination of
Available Cyanide and Total Cyanide
F. Mandatory Replacement of Mercuric
Sulfate with Copper Sulfate in Methods
for Determination of Total Kjeldahl
Nitrogen
G. Approval of Additional Standards for
Turbidity Determinations
H. Allowed Use of Capillary Columns in
EPA Methods 601–613, 624, 625, and
1624B
I. Changes to Sampling Requirements at 40
CFR Parts 122, 136, and 403
J. Approval Status of Total Elements
Digestion
K. EPA Method 245.7 for Determination of
Mercury
L. Clarification of Reporting Requirements
M. Corrections to 40 CFR Part 136, Tables
IA, IB, IC, ID, IE and Footnotes
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N. Revisions to 40 CFR Part 136, Table II
O. Corrections to Tables 40 CFR 141.23,
141.24, 141.25, and 141.74 and
Footnotes
P. Retention of Syngenta Method AG–625
for Determination of Atrazine
Q. EPA Method 327.0 for Determination of
Chlorine Dioxide
R. Deferral of Action on Microtox 1010
IV. Response to Comments
A. Use of Syngenta Method AG–625 for
Determination of Atrazine
B. Results From Use of Revised Methods,
‘‘The Determination of Radium-226 and
Radium-228 in Drinking Water by
Gamma-ray Spectrometry Using HPGE or
Ge(Li) Detectors.’’ (Revision 1.2,
December 2004)
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
A. 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
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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).
B. Safe Drinking Water Act
The Safe Drinking Water Act (SDWA),
as amended in 1996, requires EPA to
promulgate national primary drinking
water regulations (NPDWRs) that
specify maximum contaminant levels
(MCLs) or treatment techniques for
drinking water contaminants (SDWA
section 1412 (42 U.S.C. 300g–1)).
NPDWRs apply to public water systems
pursuant to SDWA sections 1401(1)(A)
(42 U.S.C. 300f(1)(A)). According to
SDWA section 1401(1)(D), NPDWRs
include ‘‘* * * criteria and procedures
to assure a supply of drinking water
which dependably complies with such
maximum contaminant levels; including
accepted methods for quality control
and testing procedures * * *’’ (42
U.S.C. 300f(1)(D)). In addition, SDWA
section 1445(a) authorizes the
Administrator to establish regulations
for monitoring to help determine
whether persons are acting in
compliance with the requirements of the
SDWA (42 U.S.C. 300j–4). EPA’s
promulgation of analytical methods for
NPDWRs is authorized under these
sections of the SDWA as well as the
general rulemaking authority in SDWA
section 1450(a) (42 U.S.C. 300j–9(a)).
The SDWA also authorizes EPA to
promulgate national secondary drinking
water regulations (NSDWRs) for
contaminants in drinking water that
primarily affect the aesthetic qualities
relating to the public acceptance of
drinking water (SDWA section 1412 (42
U.S.C. 300g–1)). These regulations are
not Federally enforceable but are
guidelines for the States (40 CFR 143.1).
The NSDWRs also include analytical
techniques for determining compliance
with the regulations (40 CFR 143.4).
EPA’s promulgation of analytical
methods for NSDWRs is authorized
under general rulemaking authority in
SDWA section 1450(a) (42 U.S.C. 300j–
9(a)).
II. Summary of Final Rule
The following sections describe the
changes EPA is making in today’s final
rule.
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A. 40 CFR Part 122
1. Some EPA Effluent Guideline
regulations, as well as EPA’s Sewage
Sludge Use and Disposal Regulations,
require the use of analytical methods
specifically prescribed by the Guideline
(see e.g. 40 CFR Part 420.21(c)). This
rule amends the National Pollutant
Discharge Elimination System (NPDES)
regulations at 40 CFR Part 122 to clarify
when an NPDES permittee must use for
its monitoring and reporting the
analytical methods specifically required
in Title 40 of the CFR, Chapter I,
Subchapters N and O (effluent
guidelines and sewage sludge,
respectively) rather than the methods in
40 CFR Part 136. The regulatory
language has been amended to explicitly
require either use of methods at 40 CFR
Part 136, or other methods that are
specifically prescribed for the particular
wastestream or for sewage sludge
monitoring requirements.
2. The rule also corrects
inconsistencies in sampling
requirements by referencing back to 40
CFR Part 136 to explicitly require use of
procedures at 40 CFR Part 136.
3. Sections 122.21(g)(7),
122.21(h)(4)(i), and 122.21(j)(4)(viii)
require an NPDES permit applicant to
report quantitative data for certain
pollutants. The rule adds E. coli and
Enterococci to the list of parameters at
40 CFR 122.21(g)(7) and 122.21(h)(4)(i),
and adds E. coli to the list of parameters
at 40 CFR 122.21(j)(4)(viii).
B. 40 CFR Part 136
This rule approves new and revised
methods for inclusion in 40 CFR Part
136. Many of those methods are from
the voluntary consensus standards body
(VCSB) that publishes Standard
Methods for the Examination of Water
and Wastewater. Those ‘‘Standard
Methods’’ are now available in both
hard copy and electronic formats. The
publisher identifies Standard Methods
in two ways, depending on the medium
of publication. Hard copy methods are
identified by the method number (e.g.,
SM 4500–Cl E) and the edition of the
manual in which they appear (e.g., 18th,
19th, 20th Editions), while the
electronic versions available on-line are
identified by the same method number
and the year the method was approved
for release (e.g., 4500–Cl E–00).
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 three new
methods submitted as alternate test
procedures for monitoring chemical
pollutants. These methods are ‘‘Test
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Method for Determination of Dissolved
Inorganic Anions in Aqueous Matrices
Using Capillary Ion Electrophoresis and
Chromate Electrolyte’’ (D6508, Rev. 2)
by Waters Corporation, ‘‘Digestion and
Distillation of Total Cyanide in Drinking
and Wastewaters using MICRO DIST
and Determination of Cyanide by Flow
Injection Analysis’’ (QuikChem Method
10–204–00–1–X) by Lachat Instruments,
and ‘‘Kelada Automated Test Methods
for Total Cyanide, Acid Dissociable
Cyanide, and Thiocyanate’’ (Kelada–01)
by Dr. Nabih Kelada.
2. The rule approves a broad purpose
digestion procedure for total recoverable
elements digestion. EPA is approving
EPA Method 200.2 (Revision 2.8, 1994)
for use with Inductively Coupled
Plasma-Atomic Emission Spectroscopy
(ICP–AES), Inductively Coupled
Plasma-Mass Spectroscopy (ICP–MS),
Stabilized Temperature Graphite
Furnace Atomic Absorption (STGFAA),
and Flame Atomic Absorption
Spectroscopy (FLAA) methods.
3. The rule approves three new multielement test procedures. The approved
methods are EPA Method 200.8
(Revision 5.4, 1994), AOAC Method
993.14 [16th Edition], and ASTM
D5673–03 for determination of elements
by ICP–MS.
4. EPA is also approving a new multielement test procedure, EPA Method
200.9 (Revision 2.2, 1994), for
determination of elements by STGFAA.
5. The rule approves four new
methods for determination of
hexavalent chromium by ion
chromatography. The methods are EPA
Method 218.6, AOAC Method 993.23
[16th Edition], and ASTM D5257–97—
SM 3500–Cr C [20th Edition] and SM
3500–Cr E [18th, 19th Editions].
6. The rule approves five new
methods for determination of anions by
ion chromatography. The methods are
EPA Method 300.0 (Revision 2.1, 1993),
EPA Method 300.1 (Revision 1.0, 1997),
AOAC Method 993.30 [16th Edition],
ASTM D4327, and SM 4110 B [18th,
19th, and 20th Editions].
7. The rule approves the use of six
automated cadmium reduction methods
to determine nitrate and nitrite
individually, as well as in combination.
The methods are EPA Method 353.2
(Revision 2.0, 1993), ASTM D3867–99
(A) and (B), SM 4500–NO3–E and F
[18th, 19th, 20th Editions] and 4500–
NO3–E and F (2000), and USGS Method
I–4545–85.
8. The rule approves a new method
for determination of chlorine by low
level amperometry—SM 4500–Cl E
[18th, 19th, 20th Editions] and SM
4500–Cl E (2000).
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9. The rule replaces EPA Method
180.1 (1978) for determination of
turbidity with EPA Method 180.1
(Revision 2.0, 1993).
10. The rule replaces EPA Method
200.7 (1990) for determination of
elements by ICP–AES with EPA Method
200.7 (Revision 4.4, 1994).
11. The rule replaces EPA Method
245.1 (1974) for determination of
mercury with EPA Method 245.1
(Revision 3.0, 1994).
12. The rule replaces EPA Method
335.3 (1978) for determination of total
cyanide with EPA Method 335.4
(Revision 1.0, 1993) with a footnote to
clarify the proper procedure for
removing sulfide interferences.
13. The rule replaces EPA Method
350.1 (1978) for determination of
ammonia with EPA Method 350.1
(Revision 2.0, 1993).
14. The rule replaces EPA Method
351.2 (1978) for determination of total
Kjeldahl nitrogen (TKN) with EPA
Method 351.2 (Revision 2.0 1993).
15. The rule replaces EPA Method
353.2 (1978) for determination of
nitrate-nitrite with EPA Method 353.2
(Revision 2.0, 1993).
16. The rule replaces EPA Method
365.1 (1978) for determination of
phosphorus (all forms) with EPA
Method 365.1 (Revision 2.0, 1993).
17. The rule replaces EPA Method
375.2 (1978) for determination of sulfate
with EPA Method 375.2 (Revision 2.0,
1993).
18. The rule replaces EPA Method
410.4 (1978) for determination of
chemical oxygen demand (COD) with
EPA Method 410.4 (Revision 2.0, 1993).
19. The rule replaces EPA Method
420.2 (1974) for determination of total
phenols with EPA Method 420.4
(Revision 1.0, 1993).
20. The rule approves a new method
for the determination of mercury, EPA
Method 245.7 ‘‘Mercury in Water by
Cold Vapor Atomic Fluorescence
Spectrometry’’ [Revision 2.0, 2005]
(EPA–821–R–05–001).
21. The rule approves a new method
for determination of available cyanide
by ligand exchange followed by flow
injection analysis, ASTM D6888–04.
22. The rule approves a new method
for determination of cations by ion
chromatography, ASTM D6919–03.
23. The rule approves a new method
for determination of chloride by
potentiometry, SM 4500–Cl–D [18th,
19th, 20th Editions] and SM 4500–Cl–D
(2000).
24. The rule approves a new method
for determination of chloride by ion
selective electrode, ASTM D512–89
(1999).
25. The rule approves two new
methods for determination of total
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cyanide by ion selective electrode, SM
4500–CN–F [18th, 19th, 20th Editions]
and SM 4500–CN–F (2000), and ASTM
D2036–98 A.
26. The rule approves two new
methods for determination of sulfide by
ion selective electrode, SM 4500–S2–G
[18th, 19th, 20th Editions] and ASTM
D4658–03 (1996).
27. The rule approves a new method
for determination of nitrate by ion
selective electrode, SM 4500–NO3–[18th,
19th, 20th Editions] and SM 4500–
NO3–(2000).
28. The rule approves an errata sheet
to correct typographical errors in the
following methods manuals, ‘‘Shortterm 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 (the ‘‘freshwater chronic
manual’’), and ‘‘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 (the ‘‘freshwater acute
manual’’).
29. The rule approves the use of
newer versions of 74 methods published
by ASTM International. The new
versions are published in the 1994,
1996, and 1999 Annual Book of ASTM
Standards Vols. 11.01 and 11.02, in the
2000 Annual Book of ASTM Standards,
Vol. 11.02 and in individual standards
published after 2000.
30. The rule approves the use of
newer versions of 88 methods published
by the Standard Methods Committee
and adopts a new numbering system to
track the approved versions of Standard
Methods. The new versions are
published in Standard Methods Online
(APHA 2003).
31. The rule approves the use of
newer versions of 19 methods published
by AOAC–International. The new
versions of these methods are published
in Official Methods of Analysis of
AOAC–International, 16th Edition,
1995.
32. The rule approves the replacement
of the mercuric sulfate catalyst with
copper sulfate in methods approved for
the determination of total Kjeldahl
nitrogen (TKN).
33. The rule approves the use of
styrene divinyl benzene beads and
stabilized formazin as alternatives to the
presently approved formazin standard
for determination of turbidity.
34. As described in the preamble to
the April 2004 proposed rule (69 FR
18213), EPA is adopting a new § 136.6
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to introduce greater flexibility in the use
of approved methods. The section
describes the circumstances in which
approved methods may be modified and
the requirements that analysts must
meet to use these modified methods in
required measurements without prior
EPA approval. The rule also includes
language at § 136.6(c) to clarify that
analysts need only meet method
performance requirements for target
analytes (those analytes being measured
for NPDES reporting) when using multianalyte methods for compliance
monitoring purposes. The rule also
includes the language at § 136.6(d) to
allow explicitly the use of capillary
(open tubular) GC columns with EPA
Methods 601–613, 624, 625, and 1624B
as alternatives to the packed GC
columns specified in those methods,
provided that analysts generate new
retention time tables with capillary
columns to be kept on file with other
information for review by auditors.
35. The rule withdraws 109 methods
contained in EPA’s ‘‘Methods for the
Chemical Analysis of Water and
Wastes’’ for which approved
alternatives published by voluntary
consensus standards bodies (e.g., ASTM
and Standard Methods) are available.
36. The rule withdraws liquid-liquid
extraction (LLE) methods, including
EPA Methods 612 and 625, as approved
procedures for determination of 1,2dichlorobenzene, 1,3-dichlorobenzene,
and 1,4-dichlorobenzene.
37. The rule withdraws approval of all
oil and grease methods that use
chlorofluorocarbon-113 (CFC–113;
Freon–113) as an extraction solvent.
38. The rule revises Table II (Required
Containers, Preservation Techniques,
and Holding Times) and the footnotes to
the table at 40 CFR 136.3(e). The table
and footnotes specify approved
sampling, preservation, and holding
time requirements for the methods
approved for compliance monitoring to
reduce confusion, resolve any conflicts
with instructions in the underlying
compliance monitoring method, and
reflect current understanding of sample
preservation requirements. The most
significant of the changes are those
made to Footnote 6, which addresses
the preservation of samples to be
analyzed for cyanide. Based on
information gathered during the
development of new cyanide methods
approved in this rulemaking, and
information collated from various
commenters and experts in cyanide
analyses, EPA revised footnote 6 to
Table II by adding text that describes
procedures that are recommended for
removal or suppression of cyanide
interferences, including interferences
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from sulfur, sulfide, sulfite, thiocyanate,
and aldehydes. The recommended
procedures may differ from those
described in the older approved
methods.
39. EPA is changing ‘‘Director of the
Environmental Monitoring Systems
Laboratory’’ and ‘‘Director, Analytical
Methods Staff’’ to ‘‘Alternate Test
Procedure Program Coordinator,
Washington, DC’’ every place the
phrases appear in the regulations. This
reflects the current organizational
structure and title for the head of EPA’s
Alternate Test Procedure (ATP) Program
management. In addition, addresses for
submission of ATPs are being updated
to reflect the current location of the
Alternate Test Procedure Program
Coordinator.
40. The rule makes other minor
editorial revisions to clarify existing
regulations.
C. 40 CFR Parts 141 and 143
1. This rule amends the regulations at
40 CFR Part 141 and Part 143 to allow
the use of 66 methods in ’’Standard
Methods Online’’ (APHA 2003) (40 CFR
141.21, 141.23, 141.74, and 143.4).
2. This rule allows the use of 28
newer versions of methods published by
ASTM International. The new versions
are published in the 1999 ‘‘Annual Book
of ASTM Standards,’’’ Vols.11.01 and
11.02, in the 2000 ‘‘Annual Book of
ASTM Standards,’’ Vol. 11.02 and in
individual standards published after
2000 (40 CFR 141.23).
3. This rule approves a new method
submitted as an alternate test procedure
for the determination of common
anions—chloride, fluoride, nitrate,
nitrite, orthophosphate, and sulfate,
‘‘Test Method for Determination of
Dissolved Inorganic Anions in Aqueous
Matrices Using Capillary Ion
Electrophoresis and Chromate
Electrolyte’’ (D6508, Rev. 2) by Waters
Corporation (40 CFR 141.23 and 143.4).
4. This rule approves two new
methods for determination of available
cyanide, ‘‘Available Cyanide by Flow
Injection, Ligand Exchange, and
Amperometry,’’ Method OIA–1677, DW
(January 2004), and ASTM D6888–04
(40 CFR 141.23).
5. This rule approves the use of EPA
Method 300.1 (Revision 1.0, 1997) for
compliance determinations of chloride,
fluoride, nitrate, nitrite, orthophosphate,
and sulfate (40 CFR 141.23 and § 143.4).
6. This rule approves the use of EPA
Method 552.3 (Revision 1.0, 2003) for
compliance determinations of dalapon
(40 CFR 141.24).
7. This rule amends 40 CFR 141.25 to
add a new method for determination of
radium-226 and radium-228. This
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method, ‘‘The Determination of Radium226 and Radium-228 in Drinking Water
by Gamma-ray Spectrometry Using
HPGE or Ge(Li) Detectors’’ (Revision
1.2, December 2004), was developed by
the Environmental Resources Center at
the Georgia Institute of Technology, and
was originally submitted to EPA as an
alternate test procedure to the currently
approved methods for determination of
radium-226 and radium-228.
8. This rule allows States the option
of approving ITS Free chlorine test
strips as a test kit for the measurement
of free chlorine using ‘‘Free Chlorine
Species’’ (HOCl- and OCl-) by Test
Strip,’’ ITS Method D99–003 (Revision
3.0, November 21, 2003) by Industrial
Test Systems, Inc. (40 CFR 141.74).
9. This rule approves EPA Method
327.0 (Revision 1.1, 2005) for
measurement of chlorine dioxide
residuals (40 CFR 141.74).
10. This rule approves the use of
styrene divinyl benzene beads and
stabilized formazin as alternatives to the
presently approved formazin standard
for determination of turbidity (40 CFR
141.74).
11. This rule revises footnote 17 to the
table at 40 CFR 141.23 to allow the use
of a 450–W UV lamp in the Kelada
Method-01 for determination of cyanide.
12. This rule allows the use of
Syngenta Method AG–625, with the
modified immunoassay testing product
manufactured by Beacon Analytical
Systems, for the measurement of
atrazine under certain conditions. It
may only be used by those systems that
do not use chlorine dioxide for drinking
water treatment. In addition, the results
of the analysis of samples with
concentrations of atrazine more than
one-half the atrazine MCL (i.e., more
than 1.5 µg/L) must be confirmed using
another approved method (40 CFR
141.24).
13. This rules also revises footnote 8
to the table in paragraph (a)(1) to correct
a long-standing discrepancy between
the footnote and the specifications in
Standard Method 9221 E. The table in
question lists Standard Method 9221 E
as one of two procedures that may be
used for monitoring fecal coliforms.
Footnote 8 simply notes the holding
time for the A–1 broth used in this
procedure. Today’s action corrects the
holding time specified in the footnote 8
to match the 7-day holding time that is
specified in Standard Method 9221 E
(40 CFR 141.74)
D. 40 CFR Part 430
This rule amends the Effluent
Limitations Guidelines for the pulp,
paper, and paperboard point source
category at 40 CFR Part 430 to approve
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a new method for determination of
chlorinated phenolics in wastewaters
generated by these industries. The rule
adds a new section, 430.02(g), to allow
the use of ‘‘Chlorinated Phenolics in
Water by In situ Acetylation and GC/MS
Determination’’ (Method CP–86.07)
developed by the National Council for
Air and Stream Improvement (NCASI)
as an alternative to otherwise required
Method 1653 in Part 430, Appendix A.
E. 40 CFR Part 455
This rule amends the regulations at 40
CFR Part 455 by moving Table 7 from
40 CFR Part 455 to 40 CFR Part 136.3(a)
as new Table IG.
F. 40 CFR Part 465
This rule amends the Effluent
Limitations Guidelines for the coil
coating point source category at 40 CFR
Part 465 to replace the method listed at
section 465.03(c) for determination of
oil and grease in wastewater samples
from all subcategories of coil coating
with EPA Method 1664A for
determination of non-polar materials
(NPM), which is generally equivalent to
total petroleum hydrocarbons.
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. Silver Determinations
EPA received comments on the
Agency’s proposed withdrawal of EPA
Method 272.1 which included
information on how to keep silver in
solution in samples with known or
suspected high levels of silver by adding
a solution containing cyanogen
chloride. As a result, EPA has added a
footnote to Table IB at § 136.3 to include
procedures for preparation and addition
of this reagent to digested samples of
this type to keep the silver in solution
for analysis by any of the approved
methods. The Agency is withdrawing
EPA Method 272.1, as proposed in April
2004 (69 FR 18183 April 6, 2004).
B. ASTM Method D5673–02 ‘‘Standard
Test Method for Elements in Water by
Inductively Coupled Plasma—Mass
Spectrometry’’
Based on comment received on the
Agency’s proposed approval of ASTM
Method D5673–02, EPA is approving an
updated version of this method ASTM
D5673–03. EPA included the updated
version of this method in a notice of
data availability (70 FR 7909, February
16, 2005) and requested public
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comment on whether it should be
approved. EPA received no adverse
comments.
C. Ammonia Determinations
EPA received comment on the
Agency’s proposed approval of an
updated version of EPA Method 350.1.
The commenter stated that mandating
the use of ethylene-diamine-tetra-acetate
(EDTA) in the method could adversely
affect method performance when using
an automated analyzer and submitted
data to support this claim. Based on
EPA’s review of the data, the Agency is
adding a footnote to Table IB at § 136.3
allowing analysts to omit EDTA from
EPA Method 350.1, provided that all of
the quality control (QC) acceptance
criteria in the method are met.
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D. Available Cyanide Determinations
The Agency solicited comment
regarding problems encountered with
the use of ligand exchangeamperometric detection methods for
determination of available cyanide in
samples that contain significant
amounts of solids and solicited
potential solutions to these problems.
Based on public comment, EPA is
adding a footnote to Table IB at § 136.3
that includes suggestions for sample
filtration and for limiting the time
between addition of ligand exchange
reagents and analysis to solve these
problems when necessary. The Agency
proposed ASTM Method D6888–03 for
determining available cyanide. Since
publication of the proposal, EPA has
received a revised version of this
method. EPA included this revised
version in a Notice of Data Availability
(NODA) and requested public comment
on the approval of this revised version
of the method (70 FR 7909, February 16,
2005). D6888–04 contains a new online
sulfide removal procedure and
represents a refinement to the proposed
version. EPA received no adverse
comments on this revised version of the
method and is approving ASTM Method
D6888–04 in today’s rule.
E. Kelada-01 Method for Determination
of Available Cyanide and Total Cyanide
Based on a comment and data
received on the Agency’s proposed
approval of the Kelada-01 method for
determination of available cyanide and
total cyanide for use in NPDES
compliance monitoring, a note has been
added at 40 CFR 136.3, Table IB,
Footnote 55 to allow the use of 450–W
UV lamp instead of the 550–W lamp
specified in the method if it provides
performance within the quality control
acceptance criteria of the method in a
given instrument. Similarly, modified
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flow cell configurations and flow
conditions may be used in the method,
provided that the QC acceptance criteria
are met. The Agency also is adding the
note at 40 CFR 141.23, Footnote 17, as
this method was previously approved
for use in drinking water compliance
monitoring.
F. Mandatory Replacement of Mercuric
Sulfate With Copper Sulfate in Methods
for Determination of Total Kjeldahl
Nitrogen
The Agency proposed the mandatory
replacement of mercury sulfate with
copper sulfate in total Kjeldahl nitrogen
(TKN) digestion. Comments expressed
concern that copper sulfate will provide
inferior performance in some samples,
and suggested that EPA allow the
continued use of mercury sulfate in
analyses, offering copper sulfate as an
option. Based on EPA’s evaluation of
these comments, the Agency has
decided that it will continue to allow
the use of mercury sulfate in TKN
analyses.
G. Approval of Additional Standards for
Turbidity Determinations
Based on comments received on the
proposed approval of additional
standards for use in methods to
determine turbidity, the Agency is
replacing turbidity standard trade
names with more generic listings in the
footnote to Table IB at § 136.3. An
example formulation for each generic
listing is also included in order to
provide a reference to at least one
source of the generic standard material.
The Agency also is adding a similar
footnote to the table in 40 CFR 141.74
where the approved methods for the
determination of turbidity in drinking
water are listed.
H. Allowed Use of Capillary Columns in
EPA Methods 601–613, 624, 625, and
1624B
The Agency proposed new language
that explicitly allows the use of
capillary columns in place of packed
columns with EPA Methods 601–613,
624, 625, and 1624B, provided that all
QC tests in these methods are performed
and all QC acceptance criteria are met.
Based on comments received on this
proposal, EPA is clarifying the
regulations at § 136.6 to state that
retention times will change with the
switch from packed to capillary
columns, so analysts are not required to
meet the retention times specified in the
method when the switch is made.
Instead, analysts must generate new
retention time tables with capillary
columns to be kept on file with other
information for review by auditors.
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I. Changes to Sampling Requirements at
40 CFR Parts 122, 136, and 403
The Agency proposed changes to the
sampling requirements specified at 40
CFR Parts 122, 136 and 403. Based on
comments received on these proposed
updates, the sampling requirements
have been modified to include clarifying
language with respect to grab and
composite sampling requirements, and
to add E. coli and Enterococci to the
parameters listed at Part 122.21 for
which an NPDES applicant must
provide analytical information. In
addition, on October 14, 2005, EPA
published in the Federal Register final
changes to its General Pretreatment
Regulations (70 FR 60134). In these
regulations, EPA consolidated
monitoring requirements for indirect
dischargers into 40 CFR 403.12(g). In the
proposal for the current rule, EPA
proposed to modify 40 CFR 403.12 (b).
Based on changes made to 40 CFR Part
403 on October 14, 2005, however, the
proposed modifications to CFR 403.12
(b) are no longer required.
J. Approval Status of Total Elements
Digestion
The Agency proposed to approve a
‘‘total recoverable’’ elements digestion
procedure, and also to retain ‘‘total’’
elements digestion for graphite furnace
atomic absorption (GFAA) analyses.
Based on comments received on this
proposal, EPA is clarifying the language
in Table IB at § 136.3 to specify Section
4.1.3 of Methods for Chemical Analysis
of Water and Wastes (MCAWW) as the
approved digestion procedure for use
with non-platform graphite furnace
atomic absorption determinations.
K. EPA Method 245.7 for Determination
of Mercury
The Agency proposed approval of
EPA Method 245.7 (December 2003) as
an additional method for determination
of mercury. Based on comments
received on this proposal, EPA has
revised the method and is approving
EPA Method 245.7 (Revision 2.0, 2005)
in this rule. Specifically, EPA has
approved the method with the following
changes: includes a discussion of the
gas-liquid separator in Section 2.6,
reduces the amount of hydrochloric acid
used during sample digestion, includes
the addition of hydrochloric acid (HCl)
to standard solutions, clarifies that
additional procedures for handling
difficult matrices may be used provided
that laboratories meet the method
performance criteria, and revises
procedures for preparing reagent blanks
to remove the addition of stannous
chloride (SnCl2) and include addition of
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HCl. EPA also has corrected section
numbering and references throughout
Sections 4 and 7 of the method.
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L. Clarification of Reporting
Requirements
The Agency proposed to add a new
§ 136.7 that would clarify that a quality
control (QC) failure does not relieve a
permittee of the duty to report results
and that results are to be reported to the
level specified in the method or
required in the permit, whichever is
lower. EPA agrees with public comment
that the proposed revision was unclear.
In this rule, EPA is revising this action
to clarify our intent in text at § 136.3,
rather than take final action on the
proposed text at § 136.7.
EPA proposed a new § 136.7
amendment to resolve conflicts between
current reporting requirements at 40
CFR Parts 122 and 125 and preservation
requirements at 40 CFR 136.3(e) and
instructions in compliance monitoring
methods specified in the tables at 40
CFR 136.3(a). For example, some
methods provide ‘‘reject tests’’ (e.g.
Method 5210 B 5-day BOD, section 6a,
Standard Methods, 20th edition) or state
that a ‘‘result may not be reported for
regulatory compliance purposes’’ (e.g.
Method OIA 1677: Available Cyanide,
section 9.3.4, OI Analytical) if an
analytical quality control measure is
outside its control limit range
(acceptance criteria). However, it may
be necessary to report such results if
resampling, reanalysis or other
corrective action is not possible. Not
reporting these results may cause a
permittee to be in violation of Part 122
or 125 reporting requirements.
Reporting such available data is
recommended as a good laboratory
practice (D3856–95 Standard Guide for
Good Laboratory Practices in
Laboratories Engaged in Sampling and
Analysis of Water, Annual Book of
ASTM Standards, Water and
Environmental Technology, Vol 11.01
Water (I), p. 353, 2003).
For clarification, in this rule, EPA is
adding a statement to the text preceding
Tables IA to IG at § 136.3(a), and Table
II at § 136.3(e) to state that reporting
requirements of Parts 122 or 125 may
take precedence over the otherwise
applicable reporting or preservation
requirements of a particular analytical
method.
M. Corrections to 40 CFR Part 136,
Tables IA, IB, IC, ID, IE and Footnotes
The Agency is correcting errors that
were published in the proposed Table
IA (List of Approved Biological
Methods), Table IB (List of Approved
Inorganic Test Procedures), Table IC
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(List of Approved Test Procedures for
Non-Pesticide Organic Compounds),
Table ID (List of Approved Test
Procedures for Pesticides), and Table IE
(List of Approved Radiologic Test
Procedures) and the footnotes to those
tables.
N. Revisions to 40 CFR Part 136, Table
II
The rule revises Table II (Required
Containers, Preservation Techniques,
and Holding Times), and the footnotes
to Table II at 40 CFR 136.3(e). The
action of updating Table II at § 136.3(e)
reflects EPA’s evaluation of comments
received on the April 6, 2004 proposal.
EPA revised footnote 1 to more clearly
distinguish between polyethylene (P),
fluoropolymer (FP), glass (G), and lowdensity polyethylene (LDPE) and has
made it explicit that a sample to be used
to determine fluoride is to be collected
in a polyethylene bottle. EPA revised
footnotes 2 and 7 to add language to
make more clear that preservation must
be within 15 minutes after collection of
a grab sample, a composite sample, or
an aliquot split from a composite
sample collected automatically over
time.
EPA modified footnote 4 to clarify the
start of holding times for the different
types of sample collection (grab
samples, composite samples collected
automatically, and a set of grab samples
that is composited in the laboratory).
The revisions remove the requirement
for collection of samples to determine
cyanide in amber glass bottles with
PTFE-lined caps from footnote 6.
Footnotes 5 and 6 describe procedures
recommended for removal or
suppression of cyanide interferences,
including interferences from oxidants,
sulfide, sulfite, thiocyanate, and
aldehydes. In addition, the footnote also
provides that other procedures for
removal or suppression of cyanide
interferences may be employed,
provided the analyst demonstrates that
such other procedures more accurately
measure cyanide.
EPA clarified requirements in
footnote 17 specific to sampling for
trace mercury, added EPA Method 245.7
to footnote 17, and removed footnote 17
from the ‘‘Preservation’’ and ‘‘Maximum
Holding Time’’ headers. EPA has
clarified footnote 18 to indicate that the
number of significant figures is intended
to establish an absolute upper limit on
sample temperature and preclude
meeting the specification through
rounding of numbers and added an
exception to footnote 18 for a sample
analyzed immediately (in less than 15
minutes from collection). EPA deleted
footnote 19 because the information is
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now in footnote 5. Deletion of this
footnote resulted in renumbering all of
the subsequent footnotes to Table II.
EPA has also clarified that
preservation is not required for soil and
sediment samples. EPA also has revised
preservation requirements for acrolein,
acrylonitrile, and purgeable aromatics to
remove inconsistences, revised
requirements for collection of samples
to be tested for Cryptosporidium and
Giardia, and established 0–8 °C as the
holding temperature for samples to be
tested for Cryptosporidium. In addition,
the Agency is correcting minor
formatting and typographical errors that
were published in the proposed Table II.
EPA recognizes that the requirements
at § 136.3 may differ from those
described in some older approved
methods and today’s action clarifies that
this section supersedes instructions in a
compliance method. Where there are
conflicts with existing methods
published by EPA, VCSBs, or other
entities, we expect that the next
revisions of these methods will conform
to the requirements at § 136.3(e).
O. Corrections to Tables 40 CFR Parts
141.23, 141.24, 141.25, and 141.74 and
Footnotes
The final rule corrects a number of
errors in the proposed tables at § 141.23
(Inorganic Chemical Sampling and
Analytical Requirements), 141.24
(Organic Chemicals, Sampling and
Analytical Requirements), 141.25
(Analytical Methods for Radioactivity)
and 141.74 (Analytical and Monitoring
Requirements) and the footnotes to
those tables. The Agency also revised
the wording of several entries for the
cyanide methods in the tables at 40 CFR
141.23 to more clearly distinguish
among the various methodologies listed
in those tables.
P. Retention of Syngenta Method AG–
625 for Determination of Atrazine
The Agency proposed to withdraw
approval of Syngenta Method AG–625
for the determination of atrazine in
drinking water. Based on comments
received regarding the April 6, 2004
proposal and comments received
regarding additional data submitted in
response to the Notice of Data
Availability (70 FR 7909, February 16,
2005), EPA has decided to retain
Syngenta Method AG–625 with some
restrictions on its use. The revised
approval requires confirmation of any
compliance monitoring results for
atrazine that are greater than one half of
the MCL for atrazine, using an alternate
approved method. EPA based its
approval on the use of the modified
immunoassay testing product produced
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by Beacon Analytical Systems, the only
version of the product that is currently
offered for sale. However, use is not
authorized for public water systems
which use chlorine dioxide for drinking
water treatment.
Q. EPA Method 327.0 for Determination
of Chlorine Dioxide
The Agency proposed to approve EPA
Method 327.0 (Revision 1.0, 2003) for
the determination of chlorine dioxide
(40 CFR 141.74). In the final rule, the
Agency has approved EPA Method
327.0 (Revision 1.1, 2005) and corrected
three typographical errors in the
proposed method.
R. Deferral of Action on Microtox 1010
Because EPA is continuing to evaluate
public comment about use of the
Microtox 1010 test procedure for
determinations of acute whole effluent
toxicity, and the data supporting use of
this test procedure, EPA is not taking
final action on the proposal to approve
Microtox 1010 for compliance
monitoring.
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IV. Response to Comments
EPA received two comments
regarding methods included in this final
rule from the August 18, 2003 proposal
(68 FR 49548), 115 comments on the
April 6, 2004 proposal (69 FR 18166),
and nine comments on the February 16,
2005 Notice of Data Availability
(NODA) (70 FR 7909). Commenters
represented a number of different
interests, including analytical
laboratories, water utilities, instrument
manufacturers, State and local
governments, trade associations,
scientists, and private citizens. A
summary of major public comments on
the proposed rules and the NODA and
the Agency’s responses is presented in
this section, and section III of this
preamble. The public docket for this
rule includes the Agency’s response to
all comments.
A. Use of Syngenta Method AG–625 for
Determination of Atrazine
EPA proposed withdrawing approval
of Syngenta Method AG–625 (Syngenta
Crop Protection Inc.) for the
determination of atrazine. Based on
comments and additional data
submitted in response to the NODA,
EPA has decided to retain Syngenta
Method AG–625 as an approved method
for atrazine, subject to certain
conditions. Today’s amended rule will
require the use of an alternate approved
method for atrazine to confirm any
results from the Syngenta method that
are greater than one half of the MCL for
atrazine. EPA’s decision to retain the
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approval of Method AG–625 is based on
using the modified immunoassay testing
product manufactured by Beacon
Analytical Systems (Atrazine Plate Kit–
Cat# CPP–004), the only version of the
product currently offered for sale.
However, based on data submitted in
response to the NODA, EPA is not
approving Method AG–625 for use
when chlorine dioxide is used for
drinking water treatment.
One commenter supported the
withdrawal of Syngenta Method AG–
625, citing EPA’s Environmental
Technology Verification (ETV) study,
and suggested that the method had not
been validated adequately prior to
EPA’s earlier approval. The commenter
also suggested that approval of a
modified version of AG–625 may be
preferable, but was concerned that the
method using the original testing
product could lead to reports of noncompliance and/or increased treatment
cost based on erroneous atrazine
measurements in the interim.
Other comments questioned the
validity of data submitted by the
American Water Works Association
(AWWA) that demonstrated method
deficiencies and requested that the data
not be considered by EPA. The
commenters noted that data were not
accompanied by suitable quality control
checks and that some tests (i.e., testing
the effect of humic acid) were not
reproducible in later studies by the
same investigator. The commenters also
suggested that data generated by AWWA
was not generated according to Method
AG–625, but rather by simply using the
commercial testing product without
reference to the method.
As reported by Adams (Adams et al.,
JAWWA, 2004, pp. 126–139), the
original immunoassay test kit used with
Method AG–625 was subject to a
positive bias in the measurement of
atrazine in the presence of disinfectants
used in drinking water treatment, such
as chlorine, monochloroamine,
chloramine T, chlorine dioxide and
other substances. Additionally, data
reported by Adams using the modified
Beacon test kit, data from the
Environmental Technology Verification
(ETV) Program, and, in fact, data in the
December 2004 Syngenta study
(Atrazine: Final Report, Syngenta
Number T006141–04, 12/10/2004),
demonstrate that test kits marketed by
Beacon, Abraxis, and SDI show a
modest positive bias in raw and finished
drinking water for most samples (i.e.,
the measured concentrations in most
samples were higher than the expected
values). For a distinct minority of
samples in these two studies, no bias or
a negative bias was shown (i.e., the
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measured concentrations were equal to
or lower than the expected
concentrations in a few samples). The
December 2004 Syngenta study
submitted to EPA demonstrated that the
modified Beacon immunoassay test kit
performed suitably in the presence of
chlorine, monochloroamine, chloramine
T, chloroform, and humic acid.
However the data show that an
interference occurred in the presence of
chlorine dioxide unless samples were
analyzed within one day of collection.
EPA agrees that data from both
Syngenta and AWWA (Adams) indicate
that, except for cases involving chlorine
dioxide, the modified testing product
performed substantially better with
regard to the positive bias and
interferences than did the original
product in the presence of disinfectants
and other interferences. EPA also agrees
that, in general, the immunoassay
products examined in these studies
exhibit some positive bias for atrazine.
Low results were only obtained from
analyses of a few samples.
EPA recognizes that a potential
positive bias is a concern for water
utilities, particularly those located in
areas such as the Midwest, where
atrazine is used extensively to control
weeds in corn and sorghum crops.
However, in many other areas, where it
is not used, atrazine is not likely to be
found in drinking water samples at all.
Because accurate information on the
occurrence of contaminants at
concentrations close to the MCL is
necessary for EPA to meet its obligation
to review MCLs every six years, EPA has
retained approval of Syngenta Method
AG–625 for atrazine with the conditions
on its use described below. The
following conditions have been added
as Footnote 5 to the table at 40 CFR
141.24(e)(1).
‘‘This method may not be used for the
analysis of atrazine in any system where
chlorine dioxide is used for drinking water
treatment. In samples from all other systems,
any result for atrazine generated by Method
AG–625 that is greater than one-half the
maximum contaminant level (MCL) (i.e.,
greater than 0.0015 mg/L or 1.5 µg/L) must
be confirmed using another approved method
for this contaminant and should use
additional volume of the original sample
collected for compliance monitoring. In
instances where a result from Method AG–
625 triggers such confirmatory testing, the
confirmatory result is to be used to determine
compliance.’’
The MCL for atrazine is 0.003 mg/L
(3 µg/L). Thus, any results from Method
AG–625 greater than 0.0015 mg/L (1.5
µg/L) must be confirmed through the
use of another approved method for
atrazine. In such instances, the
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confirmatory result is used to determine
compliance, because the methods used
for confirmatory testing are considered
more accurate.
EPA acknowledges that this
requirement for confirmation may cause
some utilities to choose not to employ
Method AG–625. However, the approval
of a method at 40 CFR Part 141 does not
constitute a requirement for its use
when other approved methods are
available. Furthermore, EPA has
concluded that, given the distribution of
atrazine use nationwide, the majority of
water utilities will not be negatively
affected by the confirmation
requirement and can take advantage of
the potential cost savings afforded by
Method AG–625 relative to other
approved methods for atrazine. EPA
notes that if utilities are monitoring for
a broad range of contaminants using
approved methods that cover multiple
analytes (e.g., Method 525.2), then the
use of a test kit may not offer a cost
advantage because of the ability to
include atrazine in a broad spectrum
method.
Based on the data provided in
response to the proposed rule and
NODA, EPA agrees that the presence of
chlorine dioxide has substantial
potential to interfere with Method AG–
625. Therefore, EPA has not approved
the method for use in water systems
where chlorine dioxide is used for
drinking water treatment. While the
data from one study suggest that the
atrazine results are not affected if
samples are analyzed within 24 hours
after sample collection, the
circumstances surrounding this
observation in the study have not been
fully characterized. At a future date,
EPA may reconsider the use of Method
AG–625 by water systems using
chlorine dioxide, if more information is
available characterizing the performance
of the method.
B. Results From Use of Revised
Methods, ‘‘The Determination of
Radium-226 and Radium-228 in
Drinking Water by Gamma-ray
Spectrometry Using HPGE or Ge(Li)
Detectors.’’ (Revision 1.2, December
2004)
The final rule establishing
radionuclide drinking water standards
published on December 7, 2000 (65 FR
76708) required drinking water systems
to sample and report on radionuclides
in their drinking water supplies during
the period from December 8, 2003 to
December 31, 2007, including the
combined result for radium-226 and
radium-228. Prior to today’s rule,
separate methods were required for the
measurement of radium-226 and
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radium-228. The separate results of the
two isotopes are summed to provide the
‘‘combined’’ result that is compared to
the MCL. One commenter supported the
approval of the method from the Georgia
Institute of Technology because one
method can be used to measure both
radium isotopes and would make for a
faster result. The commenter also noted
that there are approximately 150,000
Public Water Supply source water taps
across the country that would have to be
sampled. Given these monitoring
requirements, the commenter was
concerned about sufficient laboratory
capacity to meet the monitoring
requirements of the December 2000 rule
because approval of the Georgia
Institute of Technology method would
not become effective until promulgation
of today’s rule.
In response to this comment, EPA is
allowing community water systems to
use samples collected after January 1,
2005 and analyzed using the analytical
method approved in this rule to satisfy
the radium-226 and radium-228
monitoring requirements for the 2005–
2007 compliance period. (Minor
corrections to the method were made in
December 2004 and are reflected in the
version approved in this rule, so it was
not available for analyzing samples
collected prior to 2005.) Allowing this
early use of the method should alleviate
some of the laboratory capacity
concerns. EPA has included a footnote
in the revised table of analytical
methods for radioactivity at § 141.25 to
indicate that samples analyzed using the
newly approved method are acceptable.
Such ‘‘grandfathered’’ data must be
based on results from the analytical
method approved for use by this final
rule. The term ‘‘grandfathered data’’
used in this rule does not apply to data
collected to meet other grandfathering
provisions specified in the radionuclide
final rule that was published on
December 7, 2000 (65 FR 76708).
V. Statutory and Executive Order
Reviews
A. Executive Order 12866: Regulatory
Planning and Review
Under Executive Order 12866 (58 FR
51735, October 4, 1993), the Agency
must determine whether the regulatory
action is ‘‘significant’’ and therefore
subject to OMB review and the
requirements of the Executive Order.
The Executive Order defines
‘‘significant regulatory action’’ as one
that is likely to result in a rule that may:
(1) Have an annual effect on the
economy of $100 million or more, or
adversely affect in a material way the
economy, a sector of the economy,
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productivity, competition, jobs, the
environment, public health or safety, or
State, local, or Tribal governments or
communities;
(2) Create a serious inconsistency or
otherwise interfere with an action taken
or planned by another agency;
(3) Materially alter the budgetary
impact of entitlements, grants, user fees,
or loan programs or the rights and
obligations of recipients thereof; or
(4) Raise novel legal or policy issues
arising out of legal mandates, the
President’s priorities, or the principles
set forth in the Executive Order.
It has been determined that this rule
is not a ‘‘significant regulatory action’’
under the terms of Executive Order
12866 and is therefore not subject to
OMB review.
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
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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. The RFA provides
default definitions for each type of small
entity. It also authorizes an agency to
use alternative definitions for each
category of small entity, ‘‘which are
appropriate to the activities of the
agency’’ after proposing the alternative
definition(s) in the Federal Register and
taking comment (5 U.S.C. 601(3)–(5)). In
addition to the above, to establish an
alternative small business definition,
agencies must consult with SBA’s Chief
Counsel for Advocacy.
For purposes of assessing the impacts
of this rule on small entities for methods
under the Safe Drinking Water Act, EPA
considered small entities to be public
water systems serving 10,000 or fewer
persons. This is the cut-off level
specified by Congress in the 1996
Amendments to the Safe Drinking Water
Act for small system flexibility
provisions. In accordance with the RFA
requirements, EPA proposed using this
alternative definition in the Federal
Register (63 FR 7620, February 13,
1998), requested public comment,
consulted with the Small Business
Administration, and expressed its
intention to use the alternative
definition for all future drinking water
regulations in the Consumer Confidence
Reports regulation (63 FR 44511, August
19, 1998). As stated in that final rule,
the alternative definition would be
applied to this regulation as well.
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.
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
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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 to replace older EPA methods.
However, most laboratories that analyze
samples for EPA compliance monitoring
have already instituted QC requirements
as part of their laboratory practices. We
have determined that a small number of
small entities that are still using the
CFC–113 based oil and grease methods
may need to devote resources to analyst
training when they switch to hexanebased methods. However, due to the
decreased availability of CFC–113 in the
marketplace, we anticipate that the cost
differential, if any, will soon favor the
use of the hexane-based methods. The
phaseout of CFC–113 based methods is
required to comply with the Montreal
Protocol which prohibits the use of
CFC–113 based methods after December
31, 2005.
Although this final rule will not have
a significant economic impact on a
substantial number of small entities,
EPA nonetheless has tried to reduce the
impact of this rule on small entities.
Anticipating the prohibition of CFC–113
based methods, EPA promulgated
hexane-based methods in May 1999.
EPA has determined that most
laboratories have now switched to
hexane-based oil and grease methods,
making the analysis costs competitive
with the CFC–113 based methods.
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
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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
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G. Executive Order 13045: Protection of
Children From Environmental Health
Risks and Safety Risks
standards developed by Standard
Methods and ASTM International for
use in compliance monitoring.
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
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
F. Executive Order 13175: Consultation
and Coordination With Indian Tribal
Governments
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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.
H. Executive Order 13211: Actions That
Significantly Affect Energy Supply,
Distribution, or Use
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.
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.
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I. National Technology Transfer and
Advancement Act
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
final rule approves the use of over 150
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The Congressional Review Act, 5
U.S.C. Section 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 Section 804(2). This
rule will be effective April 11, 2007.
List of Subjects
40 CFR Part 122
Administrative practice and
procedure, Confidential business
information, Environmental protection,
Hazardous substances, Reporting and
recordkeeping requirements, Water
pollution control.
40 CFR Part 136
Environmental protection,
Incorporation by reference, Reporting
and recordkeeping requirements, Water
pollution control.
40 CFR Part 141
Chemicals, Environmental protection,
Incorporation by reference, Indianslands, Intergovernmental relations,
Radiation Protection, Reporting and
recordkeeping requirements, Water
supply.
40 CFR Part 143
Chemicals, Environmental protection,
Incorporation by reference, Indianslands, Water supply.
40 CFR Part 430
Environmental protection, Paper and
paper products industry, Reporting and
recordkeeping requirements, Waste
treatment and disposal, Water pollution
control.
40 CFR Part 455
Chemicals, Environmental protection,
Packaging and containers, Pesticides
and pests, Waste treatment and
disposal, Water pollution control.
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40 CFR Part 465
Coil coating industry, Environmental
protection, Reporting and recordkeeping
requirements, Waste treatment and
disposal, Water pollution control.
Dated: July 21, 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 122—EPA ADMINISTERED
PERMIT PROGRAMS: THE NATIONAL
POLLUTANT DISCHARGE
ELIMINATION SYSTEM
1. The authority citation for Part 122
continues to read as follows:
I
Authority: The Clean Water Act, 33 U.S.C.
1251 et seq.
2. Section 122.1 is amended by
revising paragraph (a)(4) to read as
follows:
I
§ 122.1
Purpose and Scope.
(a) * * *
(4) Regulatory provisions in Parts 125,
129, 133, 136 of this chapter and 40 CFR
subchapter N and subchapter O of this
chapter also implement the NPDES
permit program.
*
*
*
*
*
I 3. Section 122.21 is amended as
follows:
I a. By revising paragraph (g)(7)(i).
I b. By revising introductory text in
paragraph (h)(4)(i).
I c. By revising paragraph (j)(4)(viii).
§ 122.21 Application for a permit
(applicable to State programs, see § 123.25)
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*
*
*
*
*
(g) * * *
(7) Effluent characteristics. (i)
Information on the discharge of
pollutants specified in this paragraph
(g)(7) (except information on storm
water discharges which is to be
provided as specified in § 122.26).
When ‘‘quantitative data’’ for a pollutant
are required, the applicant must collect
a sample of effluent and analyze it for
the pollutant in accordance with
analytical methods approved under Part
136 of this chapter unless use of another
method is required for the pollutant
under 40 CFR subchapters N or O.
When no analytical method is approved
under Part 136 or required under
subchapters N or O, the applicant may
use any suitable method but must
provide a description of the method.
When an applicant has two or more
outfalls with substantially identical
effluents, the Director may allow the
applicant to test only one outfall and
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report that quantitative data as applying
to the substantially identical outfall.
The requirements in paragraphs
(g)(7)(vi) and (vii) of this section state
that an applicant must provide
quantitative data for certain pollutants
known or believed to be present do not
apply to pollutants present in a
discharge solely as the result of their
presence in intake water; however, an
applicant must report such pollutants as
present. When paragraph (g)(7) of this
section requires analysis of pH,
temperature, cyanide, total phenols,
residual chlorine, oil and grease, fecal
coliform (including E. coli), and
Enterococci (previously known as fecal
streptococcus at § 122.26
(d)(2)(iii)(A)(3)), or volatile organics,
grab samples must be collected for those
pollutants. For all other pollutants, a 24hour composite sample, using a
minimum of four (4) grab samples, must
be used unless specified otherwise at 40
CFR Part 136. However, a minimum of
one grab sample may be taken for
effluents from holding ponds or other
impoundments with a retention period
greater than 24 hours. In addition, for
discharges other than storm water
discharges, the Director may waive
composite sampling for any outfall for
which the applicant demonstrates that
the use of an automatic sampler is
infeasible and that the minimum of four
(4) grab samples will be a representative
sample of the effluent being discharged.
Results of analyses of individual grab
samples for any parameter may be
averaged to obtain the daily average.
Grab samples that are not required to be
analyzed immediately (see Table II at 40
CFR 136.3 (e)) may be composited in the
laboratory, provided that container,
preservation, and holding time
requirements are met (see Table II at 40
CFR 136.3 (e)) and that sample integrity
is not compromised by compositing.
*
*
*
*
*
(h) * * *
(4) * * *
(i) Quantitative data for the pollutants
or parameters listed below, unless
testing is waived by the Director. The
quantitative data may be data collected
over the past 365 days, if they remain
representative of current operations, and
must include maximum daily value,
average daily value, and number of
measurements taken. The applicant
must collect and analyze samples in
accordance with 40 CFR Part 136. When
analysis of pH, temperature, residual
chlorine, oil and grease, or fecal
coliform (including E. coli), and
Enterococci (previously known as fecal
streptococcus) and volatile organics is
required in paragraphs (h)(4)(i)(A)
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11211
through (K) of this section, grab samples
must be collected for those pollutants.
For all other pollutants, a 24-hour
composite sample, using a minimum of
four (4) grab samples, must be used
unless specified otherwise at 40 CFR
Part 136. For a composite sample, only
one analysis of the composite of aliquots
is required. New dischargers must
include estimates for the pollutants or
parameters listed below instead of
actual sampling data, along with the
source of each estimate. All levels must
be reported or estimated as
concentration and as total mass, except
for flow, pH, and temperature.
*
*
*
*
*
(j) * * *
(4) * * *
(viii) Applicants must collect samples
of effluent and analyze such samples for
pollutants in accordance with analytical
methods approved under 40 CFR Part
136 unless an alternative is specified in
the existing NPDES permit. When
analysis of pH, temperature, cyanide,
total phenols, residual chlorine, oil and
grease, fecal coliform (including E. coli),
or volatile organics is required in
paragraphs (j)(4)(ii) through (iv) of this
section, grab samples must be collected
for those pollutants. For all other
pollutants, 24-hour composite samples
must be used. For a composite sample,
only one analysis of the composite of
aliquots is required.
*
*
*
*
*
4. Section 122.41 is amended by
revising paragraphs (j)(4) and (l)(4)(ii) to
read as follows:
I
§ 122.41 Conditions applicable to all
permits (applicable to State programs, see
§ 123.25).
*
*
*
*
*
(j) * * *
(4) Monitoring must be conducted
according to test procedures approved
under 40 CFR Part 136 unless another
method is required under 40 CFR
subchapters N or O.
*
*
*
*
*
(l) * * *
(4) * * *
(ii) If the permittee monitors any
pollutant more frequently than required
by the permit using test procedures
approved under 40 CFR Part 136, or
another method required for an
industry-specific waste stream under 40
CFR subchapters N or O, the results of
such monitoring shall be included in
the calculation and reporting of the data
submitted in the DMR or sludge
reporting form specified by the Director.
*
*
*
*
*
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11212
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
5. Section 122.44 is amended by
revising paragraph (i)(1)(iv) to read as
follows:
I
a. In paragraph (a) by revising the
introductory text and Tables IA, IB, IC,
ID, and IE.
I b. In paragraph (a) by adding Table IG
after the notes of Table IF.
I c. In paragraph (b) by revising
references 6, 10, and 17, and adding
references 63 through 69.
I d. By revising paragraphs (c), (d), and
(e).
I
§ 122.44 Establishing limitations,
standards, and other permit conditions
(applicable to State NPDES programs; see
§ 123.25).
*
*
*
*
*
(i) * * *
(1) * * *
(iv) According to test procedures
approved under 40 CFR Part 136 for the
analyses of pollutants or another
method is required under 40 CFR
subchapters N or O. In the case of
pollutants for which there are no
approved methods under 40 CFR Part
136 or otherwise required under 40 CFR
subchapters N or O, monitoring must be
conducted according to a test procedure
specified in the permit for such
pollutants.
*
*
*
*
*
PART 136—GUIDELINES
ESTABLISHING TEST PROCEDURES
FOR THE ANALYSIS OF POLLUTANTS
6. The authority citation for Part 136
continues to read as follows:
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.)
7. Section 136.3 is amended as
follows:
I
§ 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, and IG. 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
IA, IB, IC, ID, IE, IF, and IG. 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. You can
get information about obtaining these
documents from the EPA Office of
Water Engineering and Analysis
Division at 202–566–1000. Documents
may be inspected at EPA’s Water
Docket, EPA West, 1301 Constitution
Avenue, NW., 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, IE, IF, and IG 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
(b) or (c) of this section or 40 CFR
401.13) other test procedures may be
used if such other test procedures have
been previously approved by the
Regional Administrator of the Region in
which the discharge will occur, and the
Director of the State in which such
discharge will occur does not object to
the use of an additional or alternate test
procedure.
TABLE IA.—LIST OF APPROVED BIOLOGICAL METHODS
Method 1
EPA
Standard
methods 18th,
19th, 20th Ed.
Most Probable Number
(MPN), 5 tube 3 dilution, or
Membrane filter (MF) 2,
single step.
MPN, 5 tube, 3 dilution,
or
p. 132 3 .............
9221C or E .......
9221C or E–99.
p. 124 3 .............
9222D ...............
9222D–97 ...........
p. 132 3 .............
9221C or E .......
9221C or E–99.
MF, single step 6 ...........
MPN, 5 tube, 3 dilution,
or
p. 124 3 .............
p. 114 3 .............
9222D ...............
9221B ...............
9222D–97.
9221B–99.
MF 2, single step or two
step.
MPN, 5 tube, 3 dilution,
or
p. 108 3 .............
9222B ...............
9222B–97 ...........
p. 114 3 .............
9221B ...............
9221B–99.
MF 2 with enrichment ....
p. 111 3 .............
9222 (B+B.5c) ..
MPN 7, 9, 15, multiple
tube,
...........................
9221B.1/
9221F12 14.
9222 (B+B.5c)–
97.
9221B.1–99/
9221F12 14.
Parameter and units
Bacteria:
1. Coliform (fecal),
number per 100
mL.
2. Coliform (fecal) in
presence of chlorine, number per
100 mL.
3. Coliform (total),
number per 100
mL.
rwilkins on PROD1PC63 with RULES
4. Coliform (total),
in presence of
chlorine, number
per 100 mL.
5. E. coli, number
per 100 mL 28.
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B–0025–
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Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
11213
TABLE IA.—LIST OF APPROVED BIOLOGICAL METHODS—Continued
EPA
Standard
methods 18th,
19th, 20th Ed.
Standard
methods online
AOAC,
ASTM,
USGS
multiple tube/multiple
well,
...........................
9223B 13 ...........
9223B–97 13 .......
991.15 11 ....
MF two step, or .............
1103.1 20 ...........
single step .....................
MPN, 5 tube, 3 dilution,
1603 21, 1604 22
p. 139 3 .............
9222B/9222G 19,
9213D.
...........................
9230B ...............
9222B–97/
9222G 19.
............................
9230B–93.
D5392–
93 10.
...................
MF 2, or .........................
p. 136 3 .............
9230C ...............
9230C–93 ...........
B–0055–
85 5.
Plate count ....................
MPN 7, 9 multiple tube, ..
p. 143 3.
...........................
9230B ...............
9230B–93.
multiple tube/multiple
well.
MF 2, 6, 7, 8, 9, two step ...
single step, or ...............
Plate count ....................
...........................
...........................
............................
1106.1 24 ...........
1600 25.
p. 143 3.
9230C ...............
9230C–93 ...........
Filtration/IMS/FA ...........
1622 26, 1623 27.
Filtration/IMS/FA ...........
1623 27.
Ceriodaphnia dubia
acute.
2002.0 29.
Daphnia puplex and
Daphnia magna acute.
Fathead Minnow,
Pimephales promelas,
and Bannerfin shiner,
Cyprinella leedsi,
acute.
Rainbow Trout,
Oncorhynchus
mykiss, and brook
trout, Salvelinus
fontinalis, acute.
Mysid, Mysidopsis
bahia, acute.
2021.0 29.
Method 1
Parameter and units
6. Fecal
streptococci,
number per 100
mL.
7. Enterococci,
number per 100
mL 28.
Protozoa:
8. Cryptosporidium 28.
9. Giardia 28 ............
Aquatic Toxicity:
10. Toxicity, acute,
fresh water organisms, LC50, percent effluent.
11. Toxicity, acute,
estuarine and
marine organisms
of the Atlantic
Ocean and Gulf
of Mexico, LC50,
percent effluent.
rwilkins on PROD1PC63 with RULES
12. Toxicity, chronic, fresh water organisms, NOEC
or IC25, percent
effluent.
Sheepshead Minnow,
Cyprinodon
variegatus, acute.
Silverside, Menidia
beryllina, Menidia
menidia, and Menidia
peninsulae, acute.
Fathead minnow,
Pimephales promelas,
larval survival and
growth.
Fathead minnow,
Pimephales promelas,
embryo-larval survival
and teratogenicity.
Daphnia, Ceriodaphnia
dubia, survival and reproduction.
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99 10.
D5259–
92 10.
2000.0 29.
2019.0 29.
2007.0 29.
2004.0 29.
2006.0 29.
1000.0 30.
1001.0 30.
1002.0 30.
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Colilert 13, 17,
Colilert18 13, 16, 17
mColiBlue-24 18
Entero-lert 13, 23
11214
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TABLE IA.—LIST OF APPROVED BIOLOGICAL METHODS—Continued
Method 1
Parameter and units
13. Toxicity, chronic, estuarine and
marine organisms
of the Atlantic
Ocean and Gulf
of Mexico, NOEC
or IC25, percent
effluent.
EPA
Standard
methods 18th,
19th, 20th Ed.
Standard
methods online
Other
Green alga,
1003.0 30.
Selenastrum
capricornutum, growth.
Sheepshead minnow,
1004.0 31.
Cyprinodon
variegatus, larval survival and growth.
Sheepshead 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.
1005.0 31.
1006.0 31.
1007.0 31.
1008.0 31.
1 The
method must be specified when results are reported.
0.45-µ 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 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.
8 When the MF method has not been used previously to test ambient 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.
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 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.
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 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.
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 or 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 Subject total coliform positive samples determined by 9222B or other membrane filter procedure to 9222G using NA MUG media.
20 USEPA. 2002. 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–02–020.
21 USEPA. 2002. 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–02–023.
22 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. 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.
23 A description of the Enterolert test may be obtained from IDEXX Laboratories, Inc., 1 IDEXX Drive, Westbrook, ME 04092.
2A
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AOAC,
ASTM,
USGS
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11215
rwilkins on PROD1PC63 with RULES
24 USEPA. 2002. 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–02–021.
25 USEPA. 2002. 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–02–022.
26 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.
27 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.
28 Recommended for enumeration of target organism in ambient water only.
29 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.
30 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.
31 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.
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4
mg/L ...............................
7. Barium—Total,4 mg/L .................................
6. Arsenic—Total,
5. Antimony—Total, 4 mg/L .............................
4. Ammonia (as N), mg/L ...............................
3.
Aluminum—Total,4
2. Alkalinity, as CaCO3, mg/L .........................
1. Acidity, as CaCO3, mg/L ............................
rwilkins on PROD1PC63 with RULES
...............................
...............................
ICP/MS ...............................................
Titration ..............................................
Electrode ............................................
350.1 60, Rev. 2.0
(1993).
Colorimetric (SDDC) ..........................
Digestion 4 followed by:
AA direct aspiration 36 ........................
AA furnace .........................................
ICP/MS ...............................................
ICP/AES 36 .........................................
AA gaseous hydride ...........................
AA furnace .........................................
STGFAA .............................................
Digestion 4 followed by .......................
ICP/MS ...............................................
ICP/AES 36 .........................................
Automated electrode ..........................
Ion Chromatography ..........................
Digestion 4 followed by:
AA direct aspiration 36 ........................
AA furnace .........................................
STGFAA .............................................
...............................
...............................
...............................
...............................
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
206.5 (Issued
1978) 1.
...............................
...............................
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
...............................
Automated phenate, or ......................
Direct Current Plasma (DCP) 36 .........
Colorimetric (Eriochrome cyanine R)
Manual, distillation (at pH 9.5) 6 followed by:
Nesslerization .....................................
ICP/AES 36 .........................................
...............................
3500–Al B .............
4500–NH3 B .........
...............................
3120 B ..................
3111 D ..................
3113 B ..................
3500–As C ...........
...............................
3120 B ..................
3114 B 4.d ............
3113 B ..................
...............................
3120 B ..................
3111 B ..................
3113 B ..................
4500–NH3 C (18th
only).
4500–NH3 C
(19th) and
4500–NH3 E
(18th).
4500–NH3 D or E
(19th) and
4500–NH3 F or
G (18th).
4500–NH3 G
(19th) and
4500–NH3 H
(18th).
...............................
...............................
...............................
...............................
3500–As B ............
...............................
3120 B ..................
...............................
...............................
...............................
3120 B ..................
...............................
...............................
...............................
...............................
4500–NH3 G .........
4500–NH3 D or E
4500–NH3 C .........
...............................
...............................
3500–Al D ............
4500–NH B3 .........
...............................
3120 B ..................
...............................
...............................
...............................
...............................
310.2 (Rev.
1974) 1.
3111 D ..................
3113 B ..................
2320 B ..................
2310 B(4a) ...........
Standard methods
(20th)
2320 B ..................
2310 B(4a) ...........
Standard methods
(18th, 19th)
3111 D–99 ..............
3113 B–99 ..............
3500–As B–97 ........
.................................
3120 B–99.
3114 B 4.d–97 ........
3113 B–99 ..............
.................................
3120 B–99.
3111 B–99.
3113 B–99.
.................................
.................................
4500–NH3 G–97 .....
4500–NH3 D or E–
97.
4500–NH3 C–97.
.................................
.................................
3500–Al B–01.
4500–NH3 B–97 ......
.................................
3120 B–99 ..............
3111 D–99 ..............
3113 B–99.
.................................
2320 B–97 ..............
2310 B(4a)–97 ........
Standard methods
online
Reference (method number or page)
...............................
...............................
EPA 35, 52
...............................
...............................
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
350.1, Rev. 2.0
(1993).
...............................
followed by:
AA direct aspiration 36 ........................
AA furnace .........................................
STGFAA .............................................
Digestion 4
Electrometric endpoint or phenolphthalein endpoint.
Electrometric or Colorimetric titration
to pH 4.5, manual, or
automatic ............................................
Methodology 58
TABLE IB.—LIST OF APPROVED INORGANIC TEST PROCEDURES
...............................
D4382–95, 02.
D2972–97, 03 (A)
D5673–03 .............
D2972–97, 03 (B)
D2972–97, 03 (C)
D5673–03 .............
...............................
D6919–03.
...............................
D1426–98, 03 (B).
D1426–98, 03 (A)
...............................
D4190–94, 99 .......
D5673–03 .............
...............................
...............................
...............................
D1067–92, 02 .......
D1067–92, 02 .......
ASTM
I–3084–85 2
I–3060–85
993.14 3
I–3062–85 2
I–4063–98 49
993.14 3
See footnote 7
I–4523–85 2
973.49 3, I–3520–
85 2
973.49 3
See footnote 34
993.143
I–4471–9750
I–3051–85 2
973.43 3, I–1030–
85 2
I–2030–85 2
I–1020–85 2
USGS/AOAC/other
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16. Chloride, mg/L ..........................................
14. Carbonaceous biochemical oxygen demand (CBOD5), mg/L 12.
15. Chemical oxygen demand (COD), mg/L ..
13. Calcium—Total,4 mg/L .............................
12. Cadmium—Total,4 mg/L ...........................
11. Bromide, mg/L ..........................................
9. Biochemical oxygen demand (BOD5), mg/
L.
10. Boron—Total,37 mg/L ...............................
8. Beryllium—Total,4 mg/L ..............................
rwilkins on PROD1PC63 with RULES
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
...............................
STGFAA .............................................
...............................
...............................
...............................
...............................
...............................
...............................
Colorimetric: manual or ......................
Automated (Ferricyanide) ..................
Potentiometric Titration ......................
Ion Selective Electrode ......................
410.3 (Rev.
1978) 1.
410.4, Rev. 2.0
(1993).
...............................
200.7, Rev. 4.4
(1994).
...............................
...............................
...............................
...............................
...............................
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
...............................
...............................
Titrimetric: (silver nitrate) or ...............
(Mercuric nitrate) ................................
Spectrophotometric, manual or automatic.
DCP, or ..............................................
Titrimetric (EDTA) ..............................
Ion Chromatography ..........................
Dissolved Oxygen Depletion with nitrification inhibitor.
Titrimetric ...........................................
................................................
Voltametry 11, or .................................
Colorimetric (Dithizone) .....................
Digestion 4 followed by:
AA direct aspiration ............................
ICP/AES .............................................
DCP 36
ICP/MS ...............................................
ICP/AES 36 .........................................
AA furnace .........................................
STGFAA .............................................
CIE/UV ...............................................
Digestion 4 followed by:
AA direct aspiration 36 ........................
DCP ....................................................
Titrimetric ...........................................
............................................................
Ion Chromatography ..........................
Colorimetric (curcumin) ......................
ICP/AES, or ........................................
DCP, or ..............................................
Colorimetric (aluminon) ......................
Dissolved Oxygen Depletion ..............
ICP/MS ...............................................
...............................
200.7, Rev. 4.4
(1994).
...............................
...............................
...............................
300.0, Rev 2.1
(1993) and
300.1, Rev 1.0
(1997).
...............................
...............................
AA furnace .........................................
ICP/AES .............................................
...............................
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
DCP 36 ................................................
Digestion 4 followed by:
AA direct aspiration ............................
ICP/MS ...............................................
ICP/AES 36 .........................................
...............................
3500–Ca B ...........
...............................
5210 B ..................
...............................
3120 B ..................
...............................
...............................
...............................
3120 B ..................
...............................
...............................
...............................
...............................
...............................
...............................
4110 B ..................
4500–B B .............
3120 B ..................
5210 B ..................
...............................
...............................
3120 B ..................
...............................
...............................
...............................
...............................
3120 B ..................
...............................
4500–Cl–E ............
4500–Cl–D ...........
...............................
4500–Cl–B ............
4500–Cl–C ...........
...............................
4500–Cl–E ............
4500–Cl–D ...........
...............................
4500–Cl–B ............
4500–Cl–C ...........
5220 D ..................
5220 C ..................
5220 D ..................
5220 C ..................
...............................
3500–Ca D ...........
...............................
5210 B ..................
3111 B ..................
3120 B ..................
...............................
...............................
3500–Cd D.
...............................
3120 B ..................
3113 B ..................
3111 B or C ..........
...............................
...............................
...............................
...............................
4110 B ..................
4500–B B .............
3120 B ..................
...............................
3500–Be D.
5210 B ..................
...............................
3120 B ..................
3113 B ..................
3111 D ..................
...............................
...............................
3120 B ..................
.................................
4500–Cl–E–97 ........
4500–Cl–D–97.
.................................
4500–Cl–B–97 ........
4500–Cl–C–97 ........
5220 D–97 ..............
5220 C–97 ..............
.................................
3500–Ca B–97 ........
.................................
5210 B–01.
3111 B–99 ..............
3120 B–99 ..............
.................................
.................................
.................................
3120 B–99 ..............
3113 B–99 ..............
3111 B or C–99 ......
.................................
.................................
.................................
.................................
4110 B–00 ..............
4500–B B–00 ..........
3120 B 99 ................
5210 B–01 ..............
.................................
.................................
3120 B–99 ..............
3113 B–99 ..............
3111 D–99 ..............
.................................
.................................
3120 B–99.
D512–89(99)(C).
...............................
...............................
D512–89(99) (B) ..
D512–89 (99) (A)
D1252–95, 00 (B)
D1252–95, 00 (A)
...............................
D511–93, 03(A).
D6919–03.
D511–93, 03(B) ....
...............................
D4190–94, 99 .......
D3557–95, 02 (C).
D5673–03 .............
...............................
D3557–95, 02 (D)
D3557–95, 02 (A
or B).
...............................
D4190–94, 99 .......
D1246–95, 99 (C)
...............................
D4327–97, 03 .......
...............................
...............................
...............................
D4190–94, 99 .......
D5673–03 .............
...............................
D3645–93 (88), 03
(A).
D3645–93 (88), 03
(B).
...............................
D5673–03 .............
973.46 3, p. 17 9 I–
3560–85 2
See footnotes 13, 14. I–
3561–85 2
I–1183–85 2
973.51 3, I–1184–
85 2
I–1187–85 2
I–2187–85 2
See footnote 34
I–3152–85 2
I–4471–97 50
See footnote 34
I–1472–852 or I–
4471–97 50
993.14 3
974.27,3 p. 37.9, I–
3135–85 2 or I–
3136–85 2
I–4138–89 51
D6508, Rev. 2 54
See footnote 34
p. S44.10
I–1125–85 2
993.30 3
973.44,3 p. 17.9, I–
1578–78 8
I–3112–85 2
I–4471–97 50
See footnote 34
993.14 3
I–4471–97 50
I–3095–85 2
See footnote 34
993.14 3
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12MRR2
22. Copper—Total,4 mg/L ...............................
21. Color, platinum cobalt units or dominant
wavelength, hue, luminance purity.
20. Cobalt—Total,4 mg/L ................................
19. Chromium—Total,4 mg/L ..........................
18. Chromium VI dissolved, mg/L ..................
17. Chlorine—Total residual, mg/L; Titrimetric
rwilkins on PROD1PC63 with RULES
DCP 36 or ...........................................
Colorimetric (Neocuproine) or ............
(Bicinchoninate) .................................
ICP/MS ...............................................
ICP/AES 36 .........................................
AA furnace .........................................
STGFAA .............................................
(Platinum cobalt), or ...........................
Spectrophotometric ............................
Digestion 4 followed by:
AA direct aspiration 36 ........................
DCP ....................................................
Colorimetric (ADMI), or ......................
ICP/MS ...............................................
ICP/AES .............................................
AA furnace .........................................
STGFAA .............................................
DCP,36 or ...........................................
Colorimetric (Diphenyl–carbazide) .....
Digestion 4 followed by:
AA direct aspiration ............................
ICP/MS ...............................................
ICP/AES 36 .........................................
AA chelation–extraction .....................
AA furnace .........................................
STGFAA .............................................
Colorimetric (Diphenyl–carbazide) .....
Digestion 4 followed by:
AA direct aspiration 36 ........................
CIE/UV ...............................................
Amperometric direct, or .....................
Amperometric direct (low level) .........
Iodometric direct ................................
Back titration ether end–point 15 or ....
DPD–FAS ...........................................
Spectrophotometric, DPD or ..............
Electrode ............................................
0.45–micron Filtration followed by:
AA chelation–extraction or .................
Ion Chromatography ..........................
Ion Chromatography ..........................
Methodology 58
...............................
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
...............................
...............................
...............................
...............................
...............................
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
...............................
...............................
...............................
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
...............................
...............................
218.6, Rev. 3.3
(1994).
...............................
300.0, Rev 2.1
(1993) and
300.1, Rev 1.0
(1997).
...............................
...............................
...............................
...............................
...............................
...............................
...............................
...............................
EPA 35, 52
...............................
3500–Cu D ...........
3500–Cu E ...........
...............................
3120 B ..................
3113 B ..................
3111 B or C ..........
2120 B ..................
2120 C ..................
...............................
2120 E ..................
...............................
3120 B ..................
3113 B ..................
3111 B or C ..........
...............................
3500–Cr D ............
...............................
3120 B ..................
3111 C ..................
3113 B ..................
3111 B ..................
3500–Cr D ............
3111 C ..................
3500–Cr E ............
...............................
4500–Cl D ............
4500–Cl E ............
4500–Cl B ............
4500–Cl C ............
4500–Cl F .............
4500–Cl G ............
...............................
4110 B ..................
Standard methods
(18th, 19th)
...............................
3500–Cu B ...........
3500–Cu C ...........
...............................
3120 B ..................
...............................
...............................
2120 B ..................
2120 C.
...............................
2120 E ..................
...............................
3120 B ..................
...............................
...............................
...............................
3500–Cr B ............
...............................
3120 B ..................
...............................
...............................
...............................
3500–Cr B ............
...............................
3500–Cr C ............
...............................
4500–Cl D ............
4500–Cl E ............
4500–Cl B ............
4500–Cl C ............
4500–Cl F .............
4500–Cl G ............
...............................
4110 B ..................
Standard methods
(20th)
.................................
3500–Cu B–99.
3500–Cu C–99 ........
.................................
3120 B–99 ..............
3113 B–99 ..............
3111 B or C–99 ......
2120 B–01 ..............
.................................
.................................
.................................
3120 B–99 ..............
3113 B–99 ..............
3111 B or C–99 ......
.................................
3500–Cr B–01.
.................................
3120 B–99.
3111 C–99.
3113 B–99 ..............
3111 B–99 ..............
3500–Cr B–01 .........
3111 C–99 ..............
3500–Cr C–01 ........
.................................
4500–Cl D–00 .........
4500–Cl E–00.
4500–Cl B–00.
4500–Cl C–00.
4500–Cl F–00.
4500–Cl G–00.
.................................
4110 B–00 ..............
Standard methods
online
Reference (method number or page)
TABLE IB.—LIST OF APPROVED INORGANIC TEST PROCEDURES—Continued
993.30 3
USGS/AOAC/other
See footnote 34
See footnote 19
...............................
993.14 3
I–4471–97 50
974.27 3 p. 37 9 I–
3270–85 2 or I–
3271–85 2
I–4274–89 51
I–1250–85 2
See footnote 34
See footnote 18
993.14 3
I–4471–97 50
p. 37 9, I–3239–
85 2
I–4243–89 51
See footnote 34
993.14 3
I–3233–93 46
974.27 3, I–3236–
85 2
I–1230–85
I–1232–85
993.23
See footnote 16
D4190–94, 99 .......
D5673–03 .............
...............................
D1688–95, 02 (C)
D1688–95, 02 (A
or B).
...............................
D4190–94, 99 .......
...............................
D5673–03 .............
...............................
D3558–94, 03 (A
or B).
D3558–94, 03 (C)
D4190–94, 99 .......
D5673–03 .............
D1687–92, 02 (C)
D1687–92, 02 (B)
D1687–92, 02 (A)
...............................
D5257–97 .............
...............................
............................... D6508, Rev. 2 54
D1253–86 (96), 03.
D4327–97, 03 .......
ASTM
11218
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12MRR2
31. Kjeldahl Nitrogen 5—Total, (as N), mg/L ..
30. Iron—Total,4 mg/L ....................................
29. Iridium—Total,4 mg/L ................................
28. Hydrogen ion (pH), pH units ....................
27. Hardness—Total, as CaCO3, mg/L ..........
26. Gold—Total,4 mg/L ...................................
25. Fluoride—Total, mg/L ...............................
24. Available Cyanide, mg/L ..........................
23. Cyanide—Total, mg/L ...............................
rwilkins on PROD1PC63 with RULES
...............................
4500–CN–F ...........
4500–CN–G ..........
...............................
...............................
...............................
Titration or ..........................................
DCP 36 or ...........................................
Colorimetric (Phenanthroline) ............
Digestion and distillation followed
by: 20
ICP/AES 36 .........................................
...............................
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
...............................
...............................
...............................
...............................
...............................
235.2 (Issued
1978) 1.
150.2 (Dec.
1982) 1.
...............................
...............................
231.2 (Rev.
1978) 1.
...............................
130.1 (Issued
1971) 1.
...............................
...............................
...............................
...............................
...............................
...............................
300.0, Rev 2.1
(1993) and
300.1, Rev 1.0
(1997).
...............................
4500–H∂ B ..........
2340 B or C ..........
...............................
...............................
...............................
4500–F–B .............
4500–F–B .............
...............................
4500–F–D .............
4500–F–E .............
4110 B ..................
...............................
...............................
...............................
3500–Fe D ...........
4500–Norg B or C
and 4500–NH3
B.
4500–NH3 C
(19th) and
4500–NH 3 E
(18th).
3120 B ..................
3113 B ..................
3111 B or C ..........
...............................
3500–Fe B ............
4500–Norg B or C
and 4500–NH3
B.
4500–NH3 C .........
3120 B ..................
...............................
...............................
...............................
...............................
3111 B ..................
...............................
4500–H∂ B ..........
2340 B or C ..........
...............................
3111 B ..................
...............................
4500–F–B .............
4500–F–B .............
...............................
4500–F–D .............
4500–F–E .............
4110 B ..................
...............................
4500–CN–D ..........
4500–CN–E ..........
...............................
...............................
4500–CN–D ..........
4500–CN–E ..........
...............................
4500–CN–C ..........
335.4, Rev. 1.0
(1993) 57.
...............................
...............................
335.4, Rev. 1.0
(1993) 57.
...............................
...............................
4500–CN–F ...........
4500–CN–G ..........
4500–CN–C ..........
...............................
...............................
AA furnace .........................................
STGFAA .............................................
Digestion 4 followed by:
AA direct aspiration 36 ........................
Digestion 4 followed by:
AA direct aspiration or .......................
AA furnace .........................................
Automated electrode ..........................
Ca plus Mg as their carbonates, by
inductively coupled plasma or AA
direct aspiration. (See Parameters
13 and 33)..
Electrometric measurement or ...........
Titrimetric (EDTA) or ..........................
DCP ....................................................
Automated colorimetric, .....................
CIE/UV ...............................................
Digestion 4 followed by:
AA direct aspiration, or ......................
AA furnace, or ....................................
Ion Selective Electrode ......................
Cyanide Amenable to Chlorination
(CATC); Manual distillation with
MgCl2 followed by Titrimetric or
Spectrophotometric.
Flow injection and ligand exchange,
followed by amperometry 61.
Automated Distillation and Colorimetry.
Manual distillation6 followed by:
Electrode, manual or ..........................
Automated ..........................................
Colorimetric, (SPADNS) or ................
Automated complexone .....................
Ion Chromatography ..........................
Automated Distillation and Colorimetry, or.
Manual distillation with MgCl2 followed by:
Titrimetric or .......................................
Spectrophotometric, manual or ..........
Automated 20 or ..................................
.................................
3500–Fe B–97 ........
4500–Norg B or C–
97 and 4500–NH3
B–97.
4500–NH3 C–97 .....
3120 B–99 ..............
3113 B–99 ..............
3111 B or C–99 ......
3111 B–99.
.................................
4500–H∂ B–00 .......
2340 B or C–97 ......
.................................
3111 B–99.
.................................
4500–F–B–97.
4500–F–C–97 ..........
.................................
4500–F–D–97 ..........
4500–F–E–97.
4110 B–00 ..............
.................................
.................................
4500–CN–F–99 .......
4500–CN–G–99 .......
4500–CN–D–99 .......
4500–CN–E–99 .......
.................................
.................................
.................................
I–4327–85 2
Kelada–01 55
OIA–1677 44
p. 22 9
I–3300–85
10–204–00–1–X 56,
I–4302–85 2
10–204–00–1–X 56
Kelada–01 55
D3590–89, 02 (A)
D4190–94, 99 .......
D1068–96, 03 (D)
D3590–89, 02 (A).
...............................
D1068–96, 03 (A
or B).
D1068–96, 03 (C).
D1293–84 (90), 99
(A or B).
...............................
D1126–86(92), 02
...............................
973.48 3
See footnote 34
See footnote 22
I–4471–97 50
974.27 3, I–3381–
85 2
973.41.3, I–1586–
85 2
See footnote21, I–
2587–852
973.5 2B 3, I–
1338–852
See footnote 34
D6508, Rev. 2 54
D4327–97,03 ........
...............................
993.30 3
D1179–93, 99 (B).
...............................
D1179–93, 99 (A).
...............................
D6888–04 .............
D2036–98(A).
D2036–98(B).
...............................
D2036–98(A) ........
...............................
D2036–98(A) ........
...............................
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12MRR2
36. Molybdenum—Total 4, mg/L .....................
35. Mercury—Total 4, mg/L .............................
34. Manganese—Total,4 mg/L ........................
33. Magnesium—Total,4 mg/L ........................
32. Lead—Total,4 mg/L ..................................
rwilkins on PROD1PC63 with RULES
...............................
EPA 35, 52
Cold vapor atomic fluorescence
spectrometry (CVAFS).
Purge and Trap CVAFS .....................
Digestion 4 followed by:
AA direct aspiration ............................
Automated ..........................................
DCP36, or ..........................................
Colorimetric (Persulfate), or ...............
(Periodate) .........................................
Cold vapor, manual or .......................
ICP/MS ...............................................
ICP/AES 36 .........................................
AA furnace .........................................
STGFAA .............................................
DCP or ...............................................
Gravimetric .........................................
Ion Chromatography ..........................
Digestion 4 followed by:
AA direct aspiration 36 ........................
ICP/AES .............................................
DCP 36 ................................................
Voltametry 11 or ..................................
Colorimetric (Dithizone) .....................
Digestion 4 followed by:
AA direct aspiration ............................
ICP/MS ...............................................
ICP/AES 36 .........................................
AA furnace .........................................
STGFAA .............................................
...............................
...............................
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
...............................
245.1, Rev. 3.0
(1994).
245.2 (Issued
1974).
245.7 Rev. 2.0
(2005) 59.
1631E 43.
...............................
200.7, Rev. 4.4
(1994).
...............................
...............................
...............................
...............................
...............................
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
...............................
3111 D ..................
...............................
3500––Mn D .........
...............................
3112 B ..................
...............................
3120 B ..................
3113 B ..................
3111 B ..................
...............................
3500–Mg D.
...............................
3120 B ..................
3111 B ..................
...............................
...............................
3500–Pb D ...........
...............................
3120 B ..................
3113 B ..................
3111 B or C ..........
...............................
...............................
...............................
...............................
...............................
...............................
...............................
.................................
...............................
...............................
3500–Mn B ...........
...............................
...............................
...............................
3120 B ..................
...............................
3111 D–99 ..............
.................................
3500–Mn B–99 .......
.................................
3112 B–99 ..............
.................................
3120 B–99 ..............
3113 B–99 ..............
3111 B–99 ..............
...............................
...............................
.................................
3120 B–99 ..............
3111 B–99 ..............
.................................
.................................
3500–Pb B–97.
.................................
3120 B–99 ..............
3113 B–99 ..............
3111 B or C–99 ......
.................................
.................................
.................................
.................................
...............................
3120 B ..................
...............................
...............................
...............................
3500–Pb B ...........
...............................
3120 B ..................
...............................
...............................
...............................
...............................
...............................
...............................
...............................
.................................
.................................
...............................
...............................
4500–NH3 D or E–
97.
.................................
Standard methods
online
4500–NH3 D or E
...............................
Standard methods
(20th)
...............................
Automated phenate colorimetric ........
Semi-automated block digestor colorimetric.
Manual or block digestor potentiometric.
Block digester, followed by Auto distillation and Titration, or.
Nesslerization, or ...............................
Flow injection gas diffusion ................
Digestion 4 followed by:
AA direct aspiration 36 ........................
Electrode ............................................
4500–NH3 C (18th
Only).
4500–NH3 F or G
(18th) and
4500–NH3 D or
E (19th).
...............................
Standard methods
(18th, 19th)
Reference (method number or page)
351.1 (Rev.
1978) 1.
351.2, Rev. 2.0
(1993).
...............................
...............................
Nesslerization or ................................
Methodology 58
TABLE IB.—LIST OF APPROVED INORGANIC TEST PROCEDURES—Continued
...............................
D4190–94, 99 .......
...............................
...............................
D3223–97, 02 .......
D5673–03 .............
...............................
D858–95, 02 (A or
B).
D858–95, 02 (C).
D6919–03.
...............................
...............................
D511–93, 03(B) ....
D4190–94, 99 .......
D3559–96, 03 (C).
D5673–03 .............
...............................
D3559–96, 03 (A
or B).
D3559–96, 03 (D)
...............................
...............................
...............................
D3590–89, 02 (A).
D3590–89, 02 (B)
...............................
D3590–89, 02 (A).
ASTM
I–3490–85 2
See footnote 34
920.203 3
See footnote 23
977.22 3, I–3462–
852
993.14 3
I–4471–97 50
974.27 3, I–3454–
85 2
See footnote 34
974.27 3, I–3447–
85 2
I–4471–97 50
See footnote 34
993.14 3
I–4471–97 50
974.27 3, I–3399–
85 2
I–4403–89 51
See footnote 40
See footnote 41
See footnote 39
I–4515–91 45
I–4551–78 8
USGS/AOAC/other
11220
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
AA furnace .........................................
ICP/AES .............................................
...............................
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
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44. Orthophosphate (as P), mg/L ...................
42. Organic carbon—Total (TOC), mg/L ........
43. Organic nitrogen (as N), mg/L .................
41. Oil and grease—Total recoverable, mg/L
40. Nitrite (as N), mg/L ...................................
39. Nitrate-nitrite (as N), mg/L ........................
...............................
353.2, Rev. 2.0
(1993).
...............................
300.0, Rev 2.1
(1993) and
300.1, Rev 1.0
(1997).
...............................
...............................
...............................
353.2, Rev. 2.0
(1993).
...............................
300.0, Rev 2.1
(1993) and
300.1, Rev 1.0
(1997).
...............................
1664A 42 ...............
CIE/UV ...............................................
Hexane extractable material (HEM):
n–Hexane extraction and gravimetry.
Silica gel treated HEM (SGT–HEM): 1664A 42.
Silica gel treatment and gravimetry..
Combustion or oxidation .................... ...............................
Total Kjeldahl N (Parameter 31)
minus ammonia N (Parameter 4).
Ascorbic acid method:.
Automated, or .................................... 365.1, Rev. 2.0
(1993).
Manual single reagent ....................... ...............................
Manual two reagent ........................... 365.3 (Issued
1978)1.
CIE/UV ...............................................
Spectrophotometric: Manual or ..........
Automated (Diazotization) ..................
Automated (*bypass cadmium reduction).
Manual (*bypass cadmium reduction)
Ion Chromatography ..........................
Automated hydrazine .........................
Ion Chromatography ..........................
Nitrate-nitrite N minus Nitrite N (See
parameters 39 and 40)..
Cadmium reduction, manual or .........
Automated, or ....................................
CIE/UV ...............................................
Ion Selective Electrode ......................
Colorimetric (Brucine sulfate), or .......
Ion Chromatography ..........................
DCP 36, or ..........................................
Colorimetric (heptoxime) ....................
ICP/MS ...............................................
300.0, Rev 2.1
(1993) and
300.1, Rev 1.0
(1997).
...............................
...............................
352.1 1 ..................
STGFAA .............................................
38. Nitrate (as N), mg/L ..................................
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
AA furnace .........................................
.........................................
...............................
DCP ....................................................
Digestion 4 followed by:
AA direct aspiration 36 ........................
37. Nickel—Total,4 mg/L .................................
ICP/AES 36
...............................
ICP/MS ...............................................
.........................................................................
rwilkins on PROD1PC63 with RULES
...............................
4500–NO2–B .........
...............................
4500–NO3–F .........
4500–NO3–H ........
4110 B ..................
4500–NO3–E .........
4500–NO3–F .........
...............................
4500–NO3 –D .......
...............................
4110 B ..................
...............................
...............................
3120 B ..................
...............................
...............................
...............................
...............................
...............................
3120 B ..................
4500–P F ..............
5310 B, C, or D ....
4500–P E .............
4500–P F ..............
5310 B, C, or D ....
...............................
5520 B 38 ..............
4500–NO3–E .........
4110 B ..................
...............................
...............................
4500–NO3–E .........
4110 B ..................
...............................
4500–NO2–B .........
...............................
4500–NO3–F .........
4500–NO3–H ........
4110 B ..................
4500–NO3–E .........
4500–NO3–F .........
...............................
4500–NO3 –D .......
...............................
...............................
3500–Ni D (17th
Edition).
4110 B ..................
...............................
3120 B ..................
3113 B ..................
3111 B or C ..........
...............................
...............................
3113 B ..................
3120 B ..................
4500–P E .............
.................................
.................................
5310 B, C, or D–00
.................................
5520 B–01 38.
4500–NO3–E–00 .....
4110 B–00 ..............
.................................
4500–NO2–B–00 .....
.................................
4500–NO3–F–00 .....
4500–NO3–H–00.
4110 B–00 ..............
4500–NO3–E–00 .....
4500–NO3–F–00 .....
.................................
4500–NO3 –D–00.
.................................
4110 B–00 ..............
.................................
.................................
3120 B–99 ..............
3113 B–99 ..............
3111 B or C–99 ......
.................................
.................................
3113 B–99 ..............
3120 B–99 ..............
D6508, Rev. 2 54
993.30 3
See footnote 34
993.14 3
I–4471–97 50
I–4503–89 51
I–3499–85 2
See footnote 34
993.14 3
I–3492–96 47
I–4471–97 50
D515–88(A) ..........
...............................
D2579–93 (A or B)
...............................
D3867–99(B).
D4327–97, 03 .......
...............................
...............................
...............................
D3867–99(A) ........
D4327–97 .............
973.56 3, I–4601–
85 2
973.55 3
973.47,3 p. 14 24
D6508, Rev.2 54
993.30 3
D6508, Rev. 2 54
See footnote 25
I–4540–85 2
I–4545–85 2
993.30 3
I–4545–85 2
...............................
D3867–99(B).
D3867–99(A) ........
973.50 3, 419D 1, 7,
p. 28 9
...............................
D4327–97, 03 .......
D4190–94, 99 .......
D5673–03 .............
...............................
D1886–90, 94 (98)
(A or B).
D1886–90, 94 (98)
(C).
...............................
D5673–03 .............
...............................
...............................
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12MRR2
60. Selenium—Total,4 mg/L ...........................
59. Ruthenium—Total,4 mg/L .........................
57. Residue—Volatile, mg/L ...........................
58. Rhodium—Total,4 mg/L ............................
56. Residue—settleable, mg/L .......................
53. Residue—Total, mg/L ...............................
54. Residue—filterable, mg/L .........................
55. Residue—non–filterable (TSS), mg/L ......
52. Potassium—Total,4 mg/L ..........................
51. Platinum—Total,4 mg/L ............................
49. Phosphorus (elemental), mg/L .................
50. Phosphorus—Total, mg/L .........................
48. Phenols, mg/L ..........................................
47. Palladium—Total,4 mg/L ...........................
46. Oxygen, dissolved, mg/L ..........................
45. Osmium—Total 4, mg/L ............................
rwilkins on PROD1PC63 with RULES
Flame photometric, or ........................
Colorimetric ........................................
Ion Chromatography ..........................
Gravimetric, 103–105° .......................
Gravimetric, 180° ...............................
Gravimetric, 103–105 °C post washing of residue.
Volumetric,
(Imhoff
cone),
or
gravimetric.
Gravimetric, 550 °C ...........................
Digestion 4 followed by:
AA direct aspiration, or ......................
AA furnace .........................................
Digestion 4 followed by:
AA direct aspiration, or ......................
AA furnace .........................................
Digestion 4 followed by:
AA furnace .........................................
ICP/AES .............................................
Digestion 4 followed by:
AA direct aspiration ............................
AA furnace .........................................
DCP ....................................................
Digestion 4 followed by:
AA direct aspiration ............................
Semi–automated block digestor ........
Automated ascorbic acid reduction ...
Gas–liquid chromatography ...............
Persulfate digestion followed by: 20
Manual or ...........................................
Automated ..........................................
Colorimetric (4AAP) manual, or .........
DCP ....................................................
Manual distillation 26 Followed by:
Electrode ............................................
Digestion 4 followed by:
AA direct aspiration, or ......................
AA furnace .........................................
Winkler (Azide modification), or .........
CIE/UV ...............................................
Digestion 4 followed by:
AA direct aspiration, or ......................
AA furnace .........................................
Ion Chromatography ..........................
Methodology 58
...............................
3111 B ..................
...............................
265.2 1.
...............................
3113 B ..................
3111 B ..................
...............................
160.4 1 ..................
3500–K D .............
...............................
...............................
2540 B ..................
2540 C ..................
2540 D ..................
3120 B ..................
3111 B ..................
...............................
...............................
...............................
...............................
2540 F ..................
3500–K B .............
...............................
...............................
2540 B ..................
2540 C ..................
2540 D ..................
3120 B ..................
...............................
...............................
...............................
2540 F ..................
...............................
267.2 1.
...............................
4500–P F ..............
...............................
4500–P B.5 ..........
4500–P E .............
...............................
...............................
...............................
...............................
...............................
4500–O G .............
4500–O C .............
...............................
...............................
4110 B ..................
Standard methods
(20th)
3111 B ..................
...............................
4500–P F ..............
...............................
4500–P B.5 ..........
4500–P E .............
...............................
...............................
...............................
3111 B ..................
...............................
4500–O G .............
4500–O C .............
3111 D ..................
...............................
4110 B ..................
Standard methods
(18th, 19th)
...............................
200.7, Rev. 4.4
(1994).
...............................
...............................
...............................
...............................
...............................
...............................
...............................
...............................
255.2 1.
...............................
...............................
253.2 1 (Issued
1978).
...............................
420.1 1 (Rev.
1978).
420.1 1 (Rev.
1978).
420.4 Rev. 1.0
(1993).
...............................
...............................
365.3 1 (Issued
1978).
365.1 Rev. 2.0
(1993).
365.4 1 (Issued
1974).
...............................
...............................
252.2 (Issued
1978) 1.
...............................
300.0, Rev 2.1
(1993) and
300.1, Rev 1.0
(1997).
...............................
EPA 35, 52
3113 B–99 ..............
3111 B–99.
3111 B–99.
.................................
2540 F–97.
3500–K B–97.
.................................
.................................
2540 B–97 ..............
2540 C–97 ..............
2540 D–97 ..............
3120 B–99.
3111 B–99 ..............
.................................
3111 B–99.
.................................
.................................
.................................
.................................
.................................
.................................
.................................
.................................
3111 B–99 ..............
.................................
4500–O G–01 .........
4500–O C–01 .........
3111 D–99.
.................................
4110 B–00 ..............
Standard methods
online
Reference (method number or page)
TABLE IB.—LIST OF APPROVED INORGANIC TEST PROCEDURES—Continued
D3859–98, 03 (B)
...............................
...............................
D6919–03.
...............................
...............................
...............................
...............................
...............................
D515–88(B) ..........
...............................
...............................
...............................
D515–88(A).
...............................
...............................
...............................
...............................
...............................
D888–92, 03 (B) ...
D888–92, 03 (A) ...
...............................
D4327–97, 03 .......
ASTM
I–4668–98 49
I–3753–85 2
I–3750–85 2
I–1750–85 2
I–3765–85 2
317 B 17
973.53 3, I–3630–
85 2
See footnote 34
973.56 3, I–4600–
85 2
I–4610–91 48
See footnote 28
973.55 3
See footnote 27
See footnote 34
See footnote 27
p. S27 10
p. S28 10
973.4 5B 3, I–
1575–78 8
I–1576–78 8
D6508, Rev. 2 54
993.30 3
USGS/AOAC/other
11222
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18:34 Mar 09, 2007
31
mg/L .............................
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12MRR2
Sulfite (as SO3), mg/L ..............................
Surfactants, mg/L .....................................
Temperature, °C .......................................
Thallium—Total, 4 mg/L ............................
71. Tin—Total,4 mg/L .....................................
67.
68.
69.
70.
66. Sulfide (as S), mg/L .................................
64. Specific conductance, micromhos/cm at
25°C.
65. Sulfate (as SO4), mg/L .............................
63. Sodium—Total,4 mg/L ..............................
62. Silver—Total,4,
61. Silica—Dissolved,37 mg/L .........................
rwilkins on PROD1PC63 with RULES
.........................................
Digestion 4 followed by:
AA direct aspiration ............................
AA furnace, or ....................................
STGFAA .............................................
ICP/MS ...............................................
ICP/AES .............................................
STGFAA .............................................
Colorimetric (methylene blue) ............
Ion Selective Electrode ......................
Titrimetric (iodine-iodate) ...................
Colorimetric (methylene blue) ............
Thermometric .....................................
Digestion 4 followed by:
AA direct aspiration ............................
AA furnace .........................................
CIE/UV ...............................................
Titrimetric (iodine), or .........................
Gravimetric .........................................
Turbidimetric ......................................
Ion Chromatography ..........................
Automated colorimetric ......................
DCP, or ..............................................
Flame photometric .............................
Ion Chromatography ..........................
Wheatstone bridge .............................
ICP/AES .............................................
DCP ....................................................
Digestion 4 followed by:
AA direct aspiration ............................
ICP/MS ...............................................
ICP/AES .............................................
AA furnace .........................................
STGFAA .............................................
Digestion 4, 29 followed by:
AA direct aspiration ............................
AA gaseous hydride ...........................
0.45 micron filtration followed by:
Colorimetric, Manual or ......................
Automated (Molybdosilicate), or ........
ICP/AES .............................................
ICP/MS ...............................................
ICP/AES 36
STGFAA .............................................
...............................
...............................
200.9, Rev. 2.2
(1994).
...............................
279.2 1 (Issued
1978).
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
...............................
...............................
...............................
200.7, Rev. 4.4
(1994).
...............................
...............................
...............................
120.1 1 (Rev.
1982).
375.2, Rev. 2.0
(1993).
...............................
...............................
300.0, Rev 2.1
(1993) and
300.1, Rev 1.0
(1997).
...............................
...............................
...............................
...............................
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
...............................
...............................
200.7, Rev. 4.4
(1994).
200.9, Rev. 2.2
(1994).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
3111 B ..................
3113 B ..................
...............................
3120 B ..................
3111 B ..................
...............................
4500–S 2–F (19th)
4500–S 2–E
(18th).
4500–S 2–D ...........
4500–S 2–G ...........
4500–SO3 2–B .......
5540 C ..................
2550 B ..................
4500–SO4 2–C or D
...............................
4110 B ..................
...............................
3500–Na D ...........
...............................
2510 B ..................
3120 B ..................
3111 B ..................
...............................
...............................
3120 B ..................
3113 B ..................
3111 B or C ..........
4500–Si D ............
...............................
3120 B ..................
3114 B ..................
...............................
3120 B ..................
...............................
...............................
...............................
3120 B ..................
3111 B–99 ..............
3113 B–99.
.................................
3120 B–99.
3111 B–99.
4500–S 2–D–00.
4500–S 2–G–00 .......
4500–SO3 2–B–00.
5540 C–00 ..............
2550 B–00 ..............
4500–S 2–D ...........
4500–S 2–G ...........
4500–SO3 2–B .......
5540 C ..................
2550 B ..................
...............................
.................................
4500–S 2–F–00 ........
.................................
.................................
4110 B–00 ..............
.................................
3500–Na B–97.
.................................
2510 B–97 ..............
3120 B–99 ..............
3111 B–99 ..............
.................................
.................................
3120 B–99 ..............
3113 B–99 ..............
3111 B or C–99 ......
4500–SiO2C–97 ......
.................................
3120 B–99 ..............
3114 B–97 ..............
.................................
3120 B–99.
...............................
4500–S 2–F ...........
4500–SO4 2–C or D
...............................
4110 B ..................
...............................
3500–Na B ...........
...............................
2510 B ..................
3120 B ..................
...............................
...............................
...............................
3120 B ..................
...............................
...............................
4500–SiO2 C ........
...............................
3120 B ..................
...............................
...............................
3120 B ..................
...............................
D5673–03 .............
D2330–88, 02.
...............................
D4658–03.
...............................
...............................
...............................
D516–90, 02 .........
D4327–97, 03 .......
D 6919–03.
D1125–95 (99) (A)
...............................
...............................
...............................
...............................
D5673–03 .............
...............................
...............................
...............................
D859–94, 00 .........
...............................
...............................
D3859–98, 03 (A)
D5673–03 .............
I–3850–78 8
993.14 3
See footnote 32
D6508, Rev. 2 54
I–3840–85 2
925.54 3
426C 30
993.30 3
973.40 3, I–2781–
85 2
See footnote 34
973.54 3, I–3735–
85 2
I–4471–97 50
See footnote 34
993.14 3
I–4471–97 50
974.27 3, p. 37 9, I–
3720–85 2
I–4724–89 51
I–1700–85 2
I–2700–85 2
I–4471–97 50
I–3667–85 2
993.14 3
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Fmt 4701
Sfmt 4700
DCP,36 or ...........................................
Colorimetric (Dithizone) or .................
(Zincon) ..............................................
ICP/MS ...............................................
ICP/AES 36 .........................................
AA furnace .........................................
DCP, or ..............................................
Colorimetric (Gallic Acid) ...................
Digestion 4 followed by:
AA direct aspiration 36 ........................
ICP/MS ...............................................
Digestion 4 followed by:
AA direct aspiration ............................
AA furnace .........................................
ICP/AES .............................................
DCP ....................................................
Nephelometric ....................................
Digestion 4 followed by:
AA direct aspiration ............................
AA furnace .........................................
ICP/AES .............................................
Methodology 58
289.2 1 (Issued
1978).
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
...............................
...............................
...............................
...............................
200.7, Rev. 4.4
(1994).
200.8, Rev. 5.4
(1994).
...............................
...............................
...............................
283.2 1 (Issued
1978).
...............................
180.1, Rev. 2.0
(1993).
200.7, Rev. 4.4
(1994).
EPA 35, 52
...............................
3500–Zn E.
3500–Zn F ............
...............................
3120 B ..................
3111 B or C ..........
...............................
3500–V D .............
...............................
3111 D ..................
...............................
3120 B ..................
...............................
2130 B ..................
3111 D ..................
Standard methods
(18th, 19th)
.................................
.................................
3120 B–99 59 ...........
3111 B or C–99 ......
.................................
3500–V B–97.
.................................
3111 D–99.
.................................
3120 B–99 ..............
.................................
2130 B–01 ..............
3111 D–99.
Standard methods
online
3500–Zn B–97 ........
...............................
...............................
3120 B ..................
...............................
...............................
3500–V B .............
...............................
...............................
...............................
3120 B ..................
...............................
2130 B ..................
...............................
Standard methods
(20th)
Reference (method number or page)
TABLE IB.—LIST OF APPROVED INORGANIC TEST PROCEDURES—Continued
3500–Zn B ............
...............................
D4190–94, 99 .......
D5673–03 .............
...............................
D1691–95, 02 (A
or B).
D4190–94, 99 .......
D5673–03 .............
D3373–93, 03.
...............................
...............................
D1889–94, 00 .......
ASTM
See footnote 33
See footnote 34
993.14 3
I–4471–97 50
974.27 3, p. 37 9, I–
3900–85 2
See footnote 34
993.14 3
I–4471–97 50
See footnote 34
I–3860–85 2
USGS/AOAC/other
Table 1B Notes:
1 ‘‘Methods for Chemical Analysis of Water and Wastes,’’ Environmental Protection Agency, Environmental Monitoring Systems Laboratory–Cincinnati (EMSL–CI), EPA–600/4–79–020 (NTIS PB 84–128677), Revised
March 1983 and 1979 where applicable.
2 Fishman, M. J., et al. ‘‘Methods for Analysis of Inorganic Substances in Water and Fluvial Sediments,’’ U.S. Department of the Interior, Techniques of Water-Resource Investigations of the U.S. Geological Survey,
Denver, CO, Revised 1989, unless otherwise stated.
3 ‘‘Official Methods of Analysis of the Association of Official Analytical Chemists,’’ Methods Manual, Sixteenth Edition, 4th Revision, 1998.
4 For the determination of total metals (which are equivalent to total recoverable metals) the sample is not filtered before processing. A digestion procedure is required to solubilize analytes in suspended material
and to break down organic-metal complexes (to convert the analyte to a detectable form for colorimetric analysis). For non–platform graphite furnace atomic absorption determinations a digestion using nitric acid (as
specified in Section 4.1.3 of Methods for the Chemical Analysis of Water and Wastes) is required prior to analysis. The procedure used should subject the sample to gentle, acid refluxing and at no time should the
sample be taken to dryness. For direct aspiration flame atomic absorption determinations (FLAA) a combination acid (nitric and hydrochloric acids) digestion is preferred prior to analysis. The approved total recoverable digestion is described as Method 200.2 in Supplement I of ‘‘Methods for the Determination of Metals in Environmental Samples’’ EPA/600R–94/111, May, 1994, and is reproduced in EPA Methods 200.7, 200.8,
and 200.9 from the same Supplement. However, when using the gaseous hydride technique or for the determination of certain elements such as antimony, arsenic, selenium, silver, and tin by non–EPA graphite furnace atomic absorption methods, mercury by cold vapor atomic absorption, the noble metals and titanium by FLAA, a specific or modified sample digestion procedure may be required and in all cases the referenced
method write–up should be consulted for specific instruction and/or cautions. For analyses using inductively coupled plasma-atomic emission spectrometry (ICP–AES), the direct current plasma (DCP) technique or the
EPA spectrochemical techniques (platform furnace AA, ICP–AES, and ICP–MS) use EPA Method 200.2 or an approved alternate procedure (e.g., CEM microwave digestion, which may be used with certain analytes
as indicated in Table IB); the total recoverable digestion procedures in EPA Methods 200.7, 200.8, and 200.9 may be used for those respective methods. Regardless of the digestion procedure, the results of the analysis after digestion procedure are reported as ‘‘total’’ metals.
5 Copper sulfate may be used in place of mercuric sulfate.
6 Manual distillation is not required if comparability data on representative effluent samples are on file to show that this preliminary distillation step is not necessary: however, manual distillation will be required to resolve any controversies.
7 Ammonia, Automated Electrode Method, Industrial Method Number 379–75 WE, dated February 19, 1976, Bran & Luebbe (Technicon) Auto Analyzer II, Bran & Luebbe Analyzing Technologies, Inc., Elmsford, NY
10523.
8 The approved method is that cited in ‘‘Methods for Determination of Inorganic Substances in Water and Fluvial Sediments’’, USGS TWRI, Book 5, Chapter A1 (1979).
9 American National Standard on Photographic Processing Effluents, April 2, 1975. Available from ANSI, 25 West 43rd st., New York, NY 10036.
10 ‘‘Selected Analytical Methods Approved and Cited by the United States Environmental Protection Agency,’’ Supplement to the Fifteenth Edition of Standard Methods for the Examination of Water and Wastewater
(1981).
11 The use of normal and differential pulse voltage ramps to increase sensitivity and resolution is acceptable.
12 Carbonaceous biochemical oxygen demand (CBOD ) must not be confused with the traditional BOD test method which measures ‘‘total BOD.’’ The addition of the nitrification inhibitor is not a procedural option,
5
5
but must be included to report the CBOD5 parameter. A discharger whose permit requires reporting the traditional BOD5 may not use a nitrification inhibitor in the procedure for reporting the results. Only when a discharger’s permit specifically states CBOD5 is required can the permittee report data using a nitrification inhibitor.
13 OIC Chemical Oxygen Demand Method, Oceanography International Corporation, 1978, 512 West Loop, P.O. Box 2980, College Station, TX 77840.
14 Chemical Oxygen Demand, Method 8000, Hach Handbook of Water Analysis, 1979, Hach Chemical Company, P.O. Box 389, Loveland, CO 80537.
75. Zinc –Total 4, mg/L ...................................
74. Vanadium—Total,4 mg/L ..........................
73. Turbidity, NTU 53 .......................................
72. Titanium—Total,4 mg/L .............................
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back titration method will be used to resolve controversy.
16 Orion Research Instruction Manual, Residual Chlorine Electrode Model 97–70, 1977, Orion Research Incorporated, 840 Memorial Drive, Cambridge, MA 02138. The calibration graph for the Orion residual chlorine
method must be derived using a reagent blank and three standard solutions, containing 0.2, 1.0, and 5.0 mL 0.00281 N potassium iodate/100 mL solution, respectively.
17 The approved method is that cited in Standard Methods for the Examination of Water and Wastewater, 14th Edition, 1976.
18 National Council of the Paper Industry for Air and Stream Improvement, Inc., Technical Bulletin 253, December 1971.
19 Copper, Biocinchoinate Method, Method 8506, Hach Handbook of Water Analysis, 1979, Hach Chemical Company, P.O. Box 389, Loveland, CO 80537.
20 When using a method with block digestion, this treatment is not required.
21 Hydrogen ion (pH) Automated Electrode Method, Industrial Method Number 378–75WA, October 1976, Bran & Luebbe (Technicon) Autoanalyzer II. Bran & Luebbe Analyzing Technologies, Inc., Elmsford, NY
10523.
22 Iron, 1,10-Phenanthroline Method, Method 8008, 1980, Hach Chemical Company, P.O. Box 389, Loveland, CO 80537.
23 Manganese, Periodate Oxidation Method, Method 8034, Hach Handbook of Wastewater Analysis, 1979, pages 2–113 and 2–117, Hach Chemical Company, Loveland, CO 80537.
24 Wershaw, R. L.,et al., ‘‘Methods for Analysis of Organic Substances in Water,’’ Techniques of Water-Resources Investigation of the U.S. Geological Survey, Book 5, Chapter A3, (1972 Revised 1987) p. 14.
25 Nitrogen, Nitrite, Method 8507, Hach Chemical Company, P.O. Box 389, Loveland, CO 80537.
26 Just prior to distillation, adjust the sulfuric-acid-preserved sample to pH 4 with 1 + 9 NaOH.
27 The approved method is cited in Standard Methods for the Examination of Water and Wastewater, 14th Edition. The colorimetric reaction is conducted at a pH of 10.0±0.2. The approved methods are given on pp
576–81 of the 14th Edition: Method 510A for distillation, Method 510B for the manual colorimetric procedure, or Method 510C for the manual spectrometric procedure.
28 R.F. Addison and R. G. Ackman, ‘‘Direct Determination of Elemental Phosphorus by Gas–Liquid Chromatography,’’ Journal of Chromatography, Vol. 47, No.3, pp. 421–426, 1970.
29 Approved methods for the analysis of silver in industrial wastewaters at concentrations of 1 mg/L and above are inadequate where silver exists as an inorganic halide. Silver halides such as the bromide and chloride are relatively insoluble in reagents such as nitric acid but are readily soluble in an aqueous buffer of sodium thiosulfate and sodium hydroxide to pH of 12. Therefore, for levels of silver above 1 mg/L, 20 mL of
sample should be diluted to 100 mL by adding 40 mL each of 2 M Na2S2O3 and NaOH. Standards should be prepared in the same manner. For levels of silver below 1 mg/L the approved method is satisfactory.
30 The approved method is that cited in Standard Methods for the Examination of Water and Wastewater, 15th Edition.
31 For samples known or suspected to contain high levels of silver (e.g., in excess of 4 mg/L), cyanogen iodide should be used to keep the silver in solution for analysis. Prepare a cyanogen iodide solution by adding 4.0 mL of concentrated NH4OH, 6.5 g of KCN, and 5.0 mL of a 1.0 N solution of I2 to 50 mL of reagent water in a volumetric flask and dilute to 100.0 mL. After digestion of the sample, adjust the pH of the
digestate to >7 to prevent the formation of HCN under acidic conditions. Add 1 mL of the cyanogen iodide solution to the sample digestate and adjust the volume to 100 mL with reagent water (NOT acid). If cyanogen
iodide is added to sample digestates, then silver standards must be prepared that contain cyanogen iodide as well. Prepare working standards by diluting a small volume of a silver stock solution with water and adjusting the pH>7 with NH4OH. Add 1 mL of the cyanogen iodide solution and let stand 1 hour. Transfer to a 100-mL volumetric flask and dilute to volume with water.
32 Stevens, H.H., Ficke, J. F., and Smoot, G. F., ‘‘Water Temperature—Influential Factors, Field Measurement and Data Presentation,’’ Techniques of Water-Resources Investigations of the U.S. Geological Survey,
Book 1, Chapter D1, 1975.
33 Zinc, Zincon Method, Method 8009, Hach Handbook of Water Analysis, 1979, pages 2–231 and 2–333, Hach Chemical Company, Loveland, CO 80537.
34 ‘‘Direct Current Plasma (DCP) Optical Emission Spectrometric Method for Trace Elemental Analysis of Water and Wastes, Method AES0029,’’ 1986—Revised 1991, Thermo Jarrell Ash Corporation, 27 Forge
Parkway, Franklin, MA 02038
35 Precision and recovery statements for the atomic absorption direct aspiration and graphite furnace methods, and for the spectrophotometric SDDC method for arsenic are provided in Appendix D of this part titled,
‘‘Precision and Recovery Statements for Methods for Measuring Metals.’’
36 Microwave-assisted digestion may be employed for this metal, when analyzed by this methodology. ‘‘Closed Vessel Microwave Digestion of Wastewater Samples for Determination of Metals’’, CEM Corporation,
P.O. Box 200, Matthews, NC 28106–0200, April 16, 1992. Available from the CEM Corporation.
37 When determining boron and silica, only plastic, PTFE, or quartz laboratory ware may be used from start until completion of analysis.
38 Only use n-hexane extraction solvent when determining Oil and Grease parameters—Hexane Extractable Material (HEM), or Silica Gel Treated HEM (analogous to EPA Method 1664A). Use of other extraction
solvents (e.g., those in the 18th and 19th editions) is prohibited.
39 Nitrogen, Total Kjeldahl, Method PAI-DK01 (Block Digestion, Steam Distillation, Titrimetric Detection), revised 12/22/94, OI Analytical/ALPKEM, P.O. Box 9010, College Station, TX 77842.
40 Nitrogen, Total Kjeldahl, Method PAI–DK02 (Block Digestion, Steam Distillation, Colorimetric Detection), revised 12/22/94, OI Analytical/ALPKEM, P.O. Box 9010, College Station, TX 77842.
41 Nitrogen, Total Kjeldahl, Method PAI–DK03 (Block Digestion, Automated FIA Gas Diffusion), revised 12/22/94, OI Analytical/ALPKEM, P.O. Box 9010, College Station, TX 77842.
42 Method 1664, Revision A ‘‘n-Hexane Extractable Material (HEM; Oil and Grease) and Silica Gel Treated n-Hexane Extractable Material (SGT-HEM; Non-polar Material) by Extraction and Gravimetry’’ EPA–821–
R–98–002, February 1999. Available at NTIS, PB–121949, U.S. Department of Commerce, 5285 Port Royal, Springfield, VA 22161.
43 USEPA. 2001. Method 1631, Revision E, ‘‘Mercury in Water by Oxidation, Purge and Trap, and Cold Vapor Atomic Fluorescence Spectrometry’’ September 2002, Office of Water, U.S. Environmental Protection
Agency (EPA–821–R–02–024). The application of clean techniques described in EPA’s draft Method 1669: Sampling Ambient Water for Trace Metals at EPA Water Quality Criteria Levels (EPA–821–R–96–011) are
recommended to preclude contamination at low-level, trace metal determinations.
44 Available Cyanide, Method OIA–1677, ‘‘Available Cyanide by Flow Injection, Ligand Exchange, and Amperometry,’’ ALPKEM, A Division of OI Analytical, P.O. Box 9010, College Station, TX 77842–9010.
45 ‘‘Methods of Analysis by the U.S. Geological Survey National Water Quality Laboratory—Determination of Ammonia Plus Organic Nitrogen by a Kjeldahl Digestion Method,’’ Open File Report (OFR) 00–170.
46 ‘‘Methods of Analysis by the U.S. Geological Survey National Water Quality Laboratory—Determination of Chromium in Water by Graphite Furnace Atomic Absorption Spectrophotometry,’’ Open File Report (OFR)
93–449.
47 ‘‘Methods of Analysis by the U.S. Geological Survey National Water Quality Laboratory—Determination of Molybdenum by Graphite Furnace Atomic Absorption Spectrophotometry,’’ Open File Report (OFR) 97–
198.
48 ‘‘Methods of Analysis by the U.S. Geological Survey National Water Quality Laboratory—Determination of Total Phosphorus by Kjeldahl Digestion Method and an Automated Colorimetric Finish That Includes Dialysis’’ Open File Report (OFR) 92–146.
49 ‘‘Methods of Analysis by the U.S. Geological Survey National Water Quality Laboratory—Determination of Arsenic and Selenium in Water and Sediment by Graphite Furnace-Atomic Absorption Spectrometry’’
Open File Report (OFR) 98–639.
50 ‘‘Methods of Analysis by the U.S. Geological Survey National Water Quality Laboratory—Determination of Elements in Whole-water Digests Using Inductively Coupled Plasma-Optical Emission Spectrometry and
Inductively Coupled Plasma-Mass Spectrometry,’’ Open File Report (OFR) 98-165.
51 ‘‘Methods of Analysis by the U.S. Geological Survey National Water Quality Laboratory—Determination of Inorganic and Organic Constituents in Water and Fluvial Sediment,’’ Open File Report (OFR) 93–125.
52 All EPA methods, excluding EPA Method 300.1, are published in ‘‘Methods for the Determination of Metals in Environmental Samples,’’ Supplement I, National Exposure Risk Laboratory-Cincinnati (NERL–CI),
EPA/600/R–94/111, May 1994; and ‘‘Methods for the Determination of Inorganic Substances in Environmental Samples,’’ NERL–CI, EPA/600/R–93/100, August, 1993. EPA Method 300.1 is available from https://
www.epa.gov/safewater/methods/pdfs/met300.pdf.
53 Styrene divinyl benzene beads (e.g. AMCO–AEPA–1 or equivalent) and stabilized formazin (e.g., Hach StablCalTM or equivalent) are acceptable substitutes for formazin.
54 Method D6508, Rev. 2, ‘‘Test Method for Determination of Dissolved Inorganic Anions in Aqueous Matrices Using Capillary Ion Electrophoresis and Chromate Electrolyte,’’ available from Waters Corp, 34 Maple
St., Milford, MA, 01757, Telephone: 508/482–2131, Fax: 508/482–3625.
55 Kelada-01, ‘‘Kelada Automated Test Methods for Total Cyanide, Acid Dissociable Cyanide, and Thiocyanate,’’ EPA 821–B–01–009, Revision 1.2, August 2001, National Technical Information Service (NTIS), 5285
Port Royal Road, Springfield, VA 22161 [Order Number PB 2001–108275]. The toll free telephone number is: 800–553–6847. Note: A 450–W UV lamp may be used in this method instead of the 550–W lamp specified
if it provides performance within the quality control (QC) acceptance criteria of the method in a given instrument. Similarly, modified flow cell configurations and flow conditions may be used in the method, provided
that the QC acceptance criteria are met.
56 QuikChem Method 10–204–00–1–X, ‘‘Digestion and Distillation of Total Cyanide in Drinking and Wastewaters using MICRO DIST and Determination of Cyanide by Flow Injection Analysis’’ is available from Lachat
Instruments 6645 W. Mill Road, Milwaukee, WI 53218, Telephone: 414–358–4200.
57 When using sulfide removal test procedures described in Method 335.4, reconstitute particulate that is filtered with the sample prior to distillation.
58 Unless otherwise stated, if the language of this table specifies a sample digestion and/or distillation ‘‘followed by’’ analysis with a method, approved digestion and/or distillation are required prior to analysis.
59 Method 245.7, Rev. 2.0, ‘‘Mercury in Water by Cold Vapor Atomic Fluorescence Spectrometry,’’ February 2005, EPA–821–R–05–001, available from the U.S. EPA Sample Control Center (operated by CSC), 6101
Stevenson Avenue, Alexandria, VA 22304, Telephone: 703–461–2100, Fax: 703–461–8056.
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use of EDTA may decrease method sensitivity in some samples. Analysts may omit EDTA provided that all method specified quality control acceptance criteria are met.
61 Samples analyzed for available cyanide using Methods OIA–1677 or D6888–04 that contain particulate matter may be filtered only after the ligand exchange reagents have been added to the samples, because
the ligand exchange process converts complexes containing available cyanide to free cyanide, which is not removed by filtration. Analysts are further cautioned to limit the time between the addition of the ligand exchange reagents and sample analysis to no more than 30 minutes to preclude settling of materials in samples.
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TABLE IC.—LIST OF APPROVED TEST PROCEDURES FOR NON-PESTICIDE ORGANIC COMPOUNDS
EPA method number 2, 7
Other approved methods
Parameter 1
GC
GC/MS
Standard Methods
[Edition(s)]
HPLC
1. Acenaphthene ...............
610
625, 1625B .....
610
2. Acenaphthylene ............
610
625, 1625B .....
610
3. Acrolein .........................
4. Acrylonitrile ....................
5. Anthracene ....................
603
603
610
624 4, 1624B.
624 4, 1624B.
625, 1625B .....
610
6. Benzene ........................
602
624, 1624B .....
........................
7. Benzidine ......................
8. Benzo(a)anthracene ......
........................
610
625 5, 1625B ..
625, 1625B .....
605
610
9. Benzo(a)pyrene .............
610
625, 1625B .....
610
10. Benzo(b)fluoranthene ..
610
625, 1625B .....
610
11. Benzo(g,h,i) perylene ..
610
625, 1625B .....
610
12. Benzo(k) fluoranthene
610
625, 1625B .....
610
........................
........................
........................
14. Benzyl butyl phthalate
606
625, 1625B .....
........................
15. Bis(2-chloroethoxy)
methane.
16. Bis(2-chloroethyl) ether
611
625, 1625B .....
........................
611
625, 1625B .....
........................
17. Bis(2-ethylhexyl)
phthalate.
18. Bromodichloro-methane.
606
625, 1625B .....
........................
601
624, 1624B .....
........................
19. Bromoform ..................
601
624, 1624B .....
........................
20. Bromomethane ............
601
624, 1624B .....
........................
21. 4-Bromophenyl phenyl
ether.
22. Carbon tetrachloride ...
611
625, 1625B .....
........................
601
624, 1624B .....
........................
13. Benzyl chloride ............
604
625, 1625B .....
........................
601, 602
624, 1624B .....
........................
25. Chloroethane ...............
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23. 4-Chloro-3-methyl phenol.
24. Chlorobenzene ............
601
624, 1624B .....
........................
26. 2-Chloroethylvinyl
ether.
601
624, 1624B .....
........................
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6440 B [18th, 19th, ...............................
20th].
6410 B, 6440 B,
6410 B–00 ............
[18th, 19th, 20th].
D4657–92 (99) .....
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 9, p.
27
...............................
6410 B–00 ............
...............................
D4657–92 (99) .....
6410 B–00 ............
D4657–92 (99) .....
6410 B–00 ............
D4657–92 (99) .....
6410 B–00 ............
D4657–92 (99) .....
6410 B–00 ............
D4657–92 (99) .....
...............................
...............................
6410 B–00 ............
...............................
6410 B–00 ............
...............................
6410 B–00 ............
...............................
6410 B–00 ............
...............................
See footnote 3, p.1
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 3, p.
130: See footnote 6, p. S102
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 9, p.
27
6410 B–00 ............
6410 B [18th, 19th,
20th].
6410 B [18th, 19th,
20th].
6410 B [18th, 19th,
20th].
6410 B [18th, 19th,
20th].
6200 C [20th] and
6230 B [18th,
19th], 6200 B
[20th] and 6210
B [18th, 19th].
6200 C [20th] and
6230 B [18th,
19th], 6200 B
[20th] and 6210
B [18th, 19th].
6200 C [20th] and
6230 B [18th,
19th], 6200 B
[20th] and 6210
B [18th, 19th].
6410 B [18th, 19th,
20th].
6200 C [20th] and
6230 B [18th,
19th].
6410 B, 6420 B
[18th, 19th, 20th].
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6220
B [18th, 19th],
6200 C [20th]
and 6230 B
[18th, 19th].
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
Sfmt 4700
D4657–92 (99) .....
Other
D4657–92 (99) .....
6410 B, 6440 B
[18th, 19th, 20th].
6200 B [20th] and
6210 B
[18th,19th], 6200
C [20th] and
6220 B
[18th,19th].
...............................
6410 B, 6440 B
[18th, 19th, 20th].
6410 B, 6440 B
[18th, 19th, 20th].
6410 B, 6440 B
[18th, 19th, 20th].
6410 B, 6440 B
[18th, 19th, 20th].
6410 B, 6440 B
[18th, 19th, 20th].
...............................
Fmt 4701
ASTM
6200 B and C–97.
6200 B and C–97.
6200 B and C–97.
6200 B and C–97.
6410 B–00 ............
...............................
6200 C–97 ............
...............................
6410 B–00, 6420
B–00.
6200 B and C–97
...............................
...............................
6200 B and C–97.
6200 B and C–97.
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See footnote 9, p.
27
See footnote 3, p.
130
See footnote 9, p.
27
See footnote 3, p.
130
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TABLE IC.—LIST OF APPROVED TEST PROCEDURES FOR NON-PESTICIDE ORGANIC COMPOUNDS—Continued
EPA method number 2, 7
Other approved methods
Parameter 1
GC/MS
GC
HPLC
Standard Methods
[Edition(s)]
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6200 B [20th] and
6210 B [18th,
19th] 6200 C
[20th] and 6230
B [18th, 19th].
6410 B [18th, 19th,
20th].
6410 B, 6420 B
[18th, 19th, 20th].
6410 B [18th, 19th,
20th].
6410 B, 6440 B
[18th, 19th, 20th].
6410 B, 6440 B
[18th, 19th, 20th].
6200 B [20th] and
6210 B [18th,
19th] 6200 C
[20th] and 6230
B [18th, 19th].
6200 C [20th] and
6220 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6200 C [20th] and
6220 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6200 C [20th] and
6220 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6410 B [18th, 19th,
20th].
6200 C [20th] and
6230 B [18th,
19th].
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6410 B, 6420 B
[18th, 19th, 20th].
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
27. Chloroform ..................
601
624, 1624B .....
........................
28. Chloromethane ............
601
624, 1624B .....
........................
29. 2-Chloronaph-thalene
612
625, 1625B .....
........................
30. 2-Chlorophenol ............
604
625, 1625B .....
........................
31. 4-Chlorophenyl phenyl
ether.
32. Chrysene .....................
611
625, 1625B .....
........................
610
625, 1625B .....
610
610
625, 1625B .....
610
601
624, 1624B .....
........................
35. 1,2-Dichloro-benzene ..
601, 602
624, 1625B .....
........................
36. 1,3-Dichloro-benzene ..
601, 602
624, 1625B .....
........................
37. 1,4-Dichloro-benzene ..
601, 602
624, 1625B .....
........................
38. 3,3-Dichloro-benzidine
........................
625, 1625B .....
605
39. Dichlorodifluoro-methane.
601
........................
........................
40. 1,1-Dichloroethane ......
601
624, 1624B .....
........................
41. 1,2-Dichloroethane ......
601
624, 1624B .....
........................
42. 1,1-Dichloroethene ......
601
624, 1624B .....
........................
43. trans-1,2-Dichloroethene.
601
624, 1624B .....
........................
44. 2,4-Dichlorophenol ......
604
625, 1625B .....
........................
45. 1,2-Dichloro-propane ..
601
624, 1624B .....
........................
46. cis-1,3-Dichloropropene.
601
624, 1624B .....
........................
Jkt 211001
PO 00000
rwilkins on PROD1PC63 with RULES
33. Dibenzo(a,h)anthracene.
34. Dibromochloro-methane.
VerDate Aug<31>2005
18:34 Mar 09, 2007
Frm 00030
Fmt 4701
Sfmt 4700
Standard Methods
Online
ASTM
6200 B and C–97
...............................
See footnote 3, p.
130
6410 B–00 ............
...............................
6410 B(00, 6420
B–00.
6410 B–00 ............
...............................
...............................
6410 B–00 ............
D4657–92 (99) .....
6410 B–00 ............
D4657–92 (99) .....
See footnote 9,
27
See footnote 9,
27
See footnote 9,
27
See footnote 9,
27
See footnote 9,
27
Other
6200 B and C–97.
p.
p.
p.
p.
p.
6200 B and C–97.
6200 C–97 ............
...............................
See footnote 9, p.
27
6200 C–97 ............
...............................
See footnote 9, p.
27
6200 C–97 ............
...............................
See footnote 9, p.
27
...............................
See footnote 9, p.
27
6410 B–00.
6200 C–97.
6200 B and C–97.
6200 B and C–97.
6200 B and C–97.
6200 B and C–97.
6410 B–00, 6420
B–00.
6200 B and C–97.
6200 B and C–97.
E:\FR\FM\12MRR2.SGM
12MRR2
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
11229
TABLE IC.—LIST OF APPROVED TEST PROCEDURES FOR NON-PESTICIDE ORGANIC COMPOUNDS—Continued
EPA method number 2, 7
Other approved methods
Parameter 1
GC/MS
GC
HPLC
Standard Methods
[Edition(s)]
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6410 B [18th, 19th,
20th].
6410 B, 6420 B
[18th, 19th, 20th].
6410 B [18th, 19th,
20th].
6410 B [18th, 19th,
20th].
6410 B [18th, 19th,
20th].
6410 B, 6420 B
[18th, 19th, 20th].
6410 B [18th, 19th,
20th].
6410 B [18th, 19th,
20th].
...............................
47. trans-1,3-Dichloropropene.
601
624, 1624B .....
........................
48. Diethyl phthalate .........
606
625, 1625B .....
........................
49. 2,4-Dimethylphenol .....
604
625, 1625B .....
........................
50. Dimethyl phthalate ......
606
625, 1625B .....
........................
51. Di-n-butyl phthalate .....
606
625, 1625B .....
........................
52. Di-n-octyl phthalate .....
606
625, 1625B .....
........................
53. 2,3-Dinitrophenol .........
604
625, 1625B .....
........................
54. 2,4-Dinitrotoluene ........
609
625, 1625B .....
........................
55. 2,6-Dinitrotoluene ........
609
625, 1625B .....
........................
56. Epichlorohydrin ...........
........................
........................
........................
57. Ethylbenzene ..............
602
624, 1624B .....
........................
58. Fluoranthene ...............
610
625, 1625B .....
610
59. Fluorene ......................
610
625, 1625B .....
610
60. 1,2,3,4,6,7,8Heptachlorodibenzofuran.
61. 1,2,3,4,7,8,9Heptachlorodibenzofuran.
62. 1,2,3,4,6,7,8Heptachlorodibenzo-pdioxin.
63. Hexachlorobenzene ....
........................
Other
6410 B–00 ............
...............................
6410 B–00, 6420
B–00.
6410 B–00 ............
...............................
6410 B–00 ............
...............................
6410 B–00 ............
...............................
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 9, p.
27
6410 B–00, 6420
B–00.
6410 B–00 ............
...............................
6410 B–00 ............
...............................
...............................
...............................
6200 B [20th] and
6200 B and C–97
6210 B [18th,
19th], 6200 C
[20th] and 6220
B [18th, 19th].
6410 B, 6440 B
6410 B–00 ............
[18th, 19th, 20th].
6410 B, 6440 B
6410 B–00 ............
[18th, 19th, 20th].
...............................
...............................
...............................
D4657–92 (99) .....
D4657–92 (99) .....
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 3, p.
130; See footnote 6, p. S102
See footnote 9, p.
27
See footnote 9, p.
27
1613B 10.
........................
1613B 10.
625, 1625B .....
........................
64. Hexachloro-butadiene
612
625, 1625B .....
........................
65. Hexachlorocyclopentadiene.
66. 1,2,3,4,7,8Hexachlorodibenzofuran.
67. 1,2,3,6,7,8Hexachlorodibenzofuran.
68. 1,2,3,7,8,9Hexachlorodibenzofuran.
69. 2,3,4,6,7,8Hexachlorodibenzofuran.
70. 1,2,3,4,7,8Hexachlorodibenzo-pdioxin.
71. 1,2,3,6,7,8Hexachlorodibenzo-pdioxin.
72. 1,2,3,7,8,9Hexachlorodibenzo-pdioxin 1613B 10.
73. Hexachloroethane .......
612
625 5, 1625B ..
........................
........................
........................
6410 B–00 ............
...............................
6410 B–00 ............
...............................
6410 B–00 ............
D4657–92 (99) .....
6410 B–00 ............
...............................
6200 C–97 ............
...............................
6410 B–00, 6420
B–00.
6410 B–00 ............
...............................
1613B 10.
........................
...............................
1613B 10.
........................
6410 B–00 ............
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 9, p.
27
1613B 10.
........................
...............................
1613B 10.
........................
6410 B–00 ............
1613B 10.
........................
6410 B [18th, 19th,
20th].
6410 B [18th, 19th,
20th].
6410 B [18th, 19th,
20th].
1613B 10.
1613B 10.
612
625, 1625B .....
........................
74. Ideno(1,2,3-cd) pyrene
610
625, 1625B .....
610
75. Isophorone ..................
rwilkins on PROD1PC63 with RULES
6200 B and C–97.
ASTM
1613B 10.
612
609
625, 1625B .....
........................
76. Methylene chloride ......
601
624, 1624B .....
........................
77. 2-Methyl-4,6dinitrophenol.
78. Naphthalene ................
604
625, 1625B .....
........................
610
625, 1625B .....
610
Jkt 211001
PO 00000
VerDate Aug<31>2005
Standard Methods
Online
18:34 Mar 09, 2007
Frm 00031
6410 B [18th, 19th,
20th].
6410 B, 6440 B
[18th, 19th, 20th].
6410 B [18th, 19th,
20th].
6200 C [20th] and
6230 B [18th,
19th].
6410 B, 6420 B
[18th, 19th, 20th].
6410 B, 6440 B
[18th, 19th, 20th].
Fmt 4701
Sfmt 4700
E:\FR\FM\12MRR2.SGM
...............................
12MRR2
See footnote 9,
27
See footnote 9,
27
See footnote 9,
27
See footnote 3,
130
p.
p.
p.
p.
See footnote 9, p.
27
See footnote 9, p.
27
11230
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
TABLE IC.—LIST OF APPROVED TEST PROCEDURES FOR NON-PESTICIDE ORGANIC COMPOUNDS—Continued
EPA method number 2, 7
Other approved methods
Parameter 1
GC
GC/MS
Standard Methods
[Edition(s)]
HPLC
79. Nitrobenzene ...............
609
625, 1625B .....
........................
80. 2-Nitrophenol ...............
604
625, 1625B .....
........................
81. 4-Nitrophenol ...............
604
625, 1625B .....
........................
82. NNitrosodimethylamine.
83. N-Nitrosodi-n-propylamine.
84. NNitrosodiphenylamine.
85.
Octachlorodibenzofuran.
86. Octachlorodibenzo-pdioxin.
87. 2,2’-Oxybis(2chloropropane) [also
known as bis(2chloroisopropyl) ether].
88. PCB–1016 ...................
607
6255, 1625B ...
........................
607
6255, 1625B ...
........................
607
6255, 1625B ...
........................
........................
ASTM
6410 B [18th,
20th].
6410 B, 6420
[18th, 19th,
6410 B, 6420
[18th, 19th,
6410 B [18th,
20th].
6410 B [18th,
20th].
6410 B [18th,
20th].
6410 B–00 ............
D4657–92 (99) .....
B
6410 B–00, 6420
20th].
B–00.
B
6410 B–00, 6420
20th].
B–00.
19th, 6410 B–00 ............
...............................
19th,
6410 B–00 ............
...............................
19th,
6410 B–00 ............
...............................
19th,
...............................
...............................
Other
See footnote 9,
27
See footnote 9,
27
See footnote 9,
27
See footnote 9,
27
See footnote 9,
27
See footnote 9,
27
p.
p.
p.
p.
p.
p.
1613B 10*.
........................
Standard Methods
Online
1613B 10.
611
625, 1625B .....
........................
6410 B [18th, 19th,
20th].
6410 B–00.
608
625 .................
........................
6410 B [18th, 19th,
20th].
6410 B–00 ............
...............................
89. PCB–1221 ...................
608
625 .................
........................
6410 B [18th, 19th,
20th].
6410 B–00 ............
...............................
90. PCB–1232 ...................
608
625 .................
........................
6410 B [18th, 19th,
20th].
6410 B–00 ............
...............................
91. PCB–1242 ...................
608
625 .................
........................
6410 B [18th, 19th,
20th].
6410 B–00 ............
...............................
92. PCB–1248 ...................
93. PCB–1254 ...................
608
608
625.
625 .................
........................
6410 B [18th, 19th,
20th].
6410 B–00 ............
...............................
See footnote 3, p.
43; See footnote
94. PCB–1260 ...................
608
625 .................
........................
6410 B, 6630 B
6410 B–00 ............
[18th, 19th, 20th].
...............................
See footnote 3, p.
43; See footnote
8
95. 1,2,3,7,8-Pentachlorodibenzofuran .
96. 2,3,4,7,8-Pentachlorodibenzofuran .
97. 1,2,3,7,8,Pentachlorodibenzo-pdioxin.
98. Pentachlorophenol ......
........................
1613B10.
........................
1613B10.
........................
1613B10.
604
625, 1625B .....
........................
6410 B, 6630 B
6410 B–00 ............
[18th, 19th, 20th].
...............................
99. Phenanthrene ..............
610
625, 1625B .....
610
D4657–92 (99) .....
100. Phenol .......................
604
625, 1625B .....
........................
101. Pyrene .......................
610
625, 1625B .....
610
6410 B,
[18th,
6410 B,
[18th,
6410 B,
[18th,
See footnote 3, p.
140; See footnote 9, p. 27
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 9, p.
27
See footnote 3, p.
43; See footnote 8
See footnote 3, p.
43; See footnote 8
See footnote 3, p.
43; See footnote 8
See footnote 3, p.
43; See footnote
8
8
........................
........................
601
613, 625 5a,
1613B 10.
624, 1624B .....
........................
601
624, 1624B .....
........................
106. Toluene .....................
602
624, 1624B .....
........................
107. 1,2,4-Trichloro-benzene.
612
625, 1625B .....
........................
Jkt 211001
PO 00000
B
6410 B–00 ............
20th].
B
6410 B–00, 6420
20th].
B–00.
B
6410 B–00 ............
20th].
...............................
D4657–92 (99) .....
1613B10.
105. Tetrachloroethene .....
rwilkins on PROD1PC63 with RULES
102. 2,3,7,8-Tetrachlorodibenzofuran.
103. 2,3,7,8-Tetrachlorodibenzo-p-dioxin.
104. 1,1,2,2-Tetra-chloro
ethane .
6440
19th,
6420
19th,
6440
19th,
VerDate Aug<31>2005
18:34 Mar 09, 2007
Frm 00032
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6220
B [18th, 19th].
6410 B [18th, 19th,
20th].
Fmt 4701
Sfmt 4700
6200 B and C–97
...............................
See footnote 3, p.
130
6200 B and C–97
...............................
See footnote 3, p.
130
...............................
See footnote 3, p.
130; See footnote 9, p. 27
6200 B and C–97.
6410 B–00 ............
E:\FR\FM\12MRR2.SGM
12MRR2
11231
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
TABLE IC.—LIST OF APPROVED TEST PROCEDURES FOR NON-PESTICIDE ORGANIC COMPOUNDS—Continued
EPA method number 2, 7
Other approved methods
Parameter 1
GC/MS
GC
HPLC
Standard Methods
[Edition(s)]
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6200 B and C–97
6200 B and C–97.
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6200 B [20th] and
6210 B [18th,
19th], 6200 C
[20th] and 6230
B [18th, 19th].
6410 B, 6420 B
[18th, 19th, 20th].
6200 B [20th] and
6210 B [18th,
19th], ≤6200 C
[20th] and 6230
B [18th, 19th].
6200 B and C–97.
108. 1,1,1-Trichloro-ethane
601
624, 1624B .....
........................
109. 1,1,2-Trichloro-ethane
601
624, 1624B .....
110. Trichloroethene .........
601
624, 1624B .....
6200 B [20th]
and 6210 B
[18th, 19th],
6200 C [20th]
and 6230 B
[18th, 19th]
........................
111. Trichlorofluoro-methane.
601
624 .................
........................
112. 2,4,6-Trichlorophenol
604
625, 1625B .....
........................
113. Vinyl chloride .............
601
624, 1624B .....
........................
Standard Methods
Online
...............................
ASTM
Other
See footnote 3, p.
130.
6200 B and C–97.
6410 B–00, 6420
B–00.
6200 B and C–97.
...............................
See footnote 9, p.
27
1 All
parameters are expressed in micrograms per liter (µg/L) except for Method 1613B in which the parameters are expressed in picograms per liter (pg/L).
full text of Methods 601–613, 624, 625, 1624B, and 1625B, are given at Appendix A, ‘‘Test Procedures for Analysis of Organic Pollutants,’’ of this Part 136.
The full text of Method 1613B is incorporated by reference into this Part 136 and is available from the National Technical Information Services as stock number
PB95–104774. The standardized test procedure to be used to determine the method detection limit (MDL) for these test procedures is given at Appendix B, ‘‘Definition and Procedure for the Determination of the Method Detection Limit,’’ of this Part 136.
3 ‘‘Methods for Benzidine: Chlorinated Organic Compounds, Pentachlorophenol and Pesticides in Water and Wastewater,’’ U.S. Environmental Protection Agency,
September, 1978.
4 Method 624 may be extended to screen samples for Acrolein and Acrylonitrile. However, when they are known to be present, the preferred method for these two
compounds is Method 603 or Method 1624B.
5 Method 625 may be extended to include benzidine, hexachlorocyclopentadiene, N-nitrosodimethylamine, and N-nitrosodiphenylamine. However, when they are
known to be present, Methods 605, 607, and 612, or Method 1625B, are preferred methods for these compounds.
5a 625, screening only.
6 ‘‘Selected Analytical Methods Approved and Cited by the United States Environmental Protection Agency,’’ Supplement to the Fifteenth Edition of Standard Methods for the Examination of Water and Wastewater (1981).
7 Each analyst must make an initial, one-time demonstration of their ability to generate acceptable precision and accuracy with Methods 601–603, 624, 625, 1624B,
and 1625B (See Appendix A of this Part 136) in accordance with procedures each in Section 8.2 of each of these methods. Additionally, each laboratory, on an ongoing basis must spike and analyze 10% (5% for methods 624 and 625 and 100% for methods 1624B and 1625B) of all samples to monitor and evaluate laboratory
data quality in accordance with Sections 8.3 and 8.4 of these methods. When the recovery of any parameter falls outside the warning limits, the analytical results for
that parameter in the unspiked sample are suspect. The results should be reported, but cannot be used to demonstrate regulatory compliance. These quality control
requirements also apply to the Standard Methods, ASTM Methods, and other methods cited.
8 ‘‘Organochlorine Pesticides and PCBs in Wastewater Using EmporeTM Disk’’ 3M Corporation Revised 10/28/94.
9 USGS Method 0–3116–87 from ‘‘Methods of Analysis by U.S. Geological Survey National Water Quality Laboratory—Determination of Inorganic and Organic Constituents in Water and Fluvial Sediments,’’ U.S. Geological Survey, Open File Report 93–125.
10 Analysts may use Fluid Management Systems, Inc. PowerPrep system in place of manual cleanup provided that the analysis meet the requirements of Method
1613B (as specified in Section 9 of the method) and permitting authorities.
2 The
TABLE ID.—LIST OF APPROVED TEST PROCEDURES FOR PESTICIDES 1
EPA 2, 7
Standard Methods
18th, 19th, 20th Ed.
Standard Methods
Online
Method
1. Aldrin ..............................
GC ..................
608
6630 B & C ..........
..........................
GC/MS ...........
GC ..................
625
2. Ametryn ..........................
6410 B ..................
...............................
3. Aminocarb ......................
TLC ................
4. Atraton ............................
ASTM
Other
D3086–90, ............
D5812-96 (2002) ..
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 8
6410 B–00.
...............................
...............................
...............................
...............................
...............................
GC ..................
...............................
...............................
...............................
5. Atrazine ..........................
GC ..................
...............................
...............................
...............................
6. Azinphos methyl .............
GC ..................
...............................
...............................
...............................
7. Barban ............................
rwilkins on PROD1PC63 with RULES
Parameter
TLC ................
...............................
...............................
...............................
8. a–BHC ...........................
GC ..................
608
6630 B & C ..........
..........................
D3086–90, ............
D5812–96(02) ......
See footnote 3, p. 83; See footnote 6,
p S68
See footnote 3, p. 94; See footnote 6,
p. S16
See footnote 3, p. 83; See footnote 6,
p. S68
See footnote 3, p. 83; See footnote 6,
p. S68; See footnote 9
See footnote 3, p. 25; See footnote 6,
p. S51
See footnote 3, p. 104; See footnote 6,
p. S64
See footnote 3, p. 7; See footnote 8
9. b–BHC ............................
GC/MS ...........
GC ..................
625 5
608
6410 B ..................
6630 C ..................
6410 B–00.
..........................
GC/MS ...........
625 5
6410 B ..................
6410 B–00.
VerDate Aug<31>2005
18:34 Mar 09, 2007
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PO 00000
Frm 00033
Fmt 4701
Sfmt 4700
D3086–90, ............
D5812–96(02) ......
E:\FR\FM\12MRR2.SGM
See footnote 8
12MRR2
11232
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
TABLE ID.—LIST OF APPROVED TEST PROCEDURES FOR PESTICIDES 1—Continued
EPA 2, 7
Standard Methods
18th, 19th, 20th Ed.
Standard Methods
Online
Parameter
Method
10. d–BHC ..........................
GC ..................
608
6630 C ..................
..........................
11. g-BHC (Lindane) ...........
GC/MS ...........
GC ..................
625 5
608
6410 B ..................
6630 B & C ..........
6410 B–00.
..........................
625
6410 B ..................
6410 B–00.
12. Captan ..........................
GC/MS ...........
.
GC ..................
....................
6630 B ..................
...............................
13. Carbaryl ........................
TLC ................
....................
...............................
14. Carbo-phenothion .........
GC ..................
....................
15. Chlordane .....................
GC ..................
16. Chloro-propham ...........
ASTM
Other
D3086–90, ............
D5812–96(02) ......
See footnote 8
D3086–90, ............
D5812–96(02) ......
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 8
See footnote 3, p. 7
...............................
D3086–90, ............
D5812–96(02) ......
...............................
...............................
...............................
...............................
608
6630 B & C ..........
...............................
D3086–90, ............
D5812–96(02) ......
GC/MS ...........
TLC ................
625
....................
6410 B ..................
...............................
6410 B–00.
...............................
...............................
17. 2,4-D .............................
GC ..................
....................
6640 B ..................
...............................
...............................
18. 4,4′-DDD ......................
GC ..................
608
6630 B & C ..........
...............................
D3086–90, ............
D5812–96(02) ......
See footnote 3, p. 104; See footnote 6,
p. S64.
See footnote 3, p. 115; See footnote 4,
p. 40
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 8
19. 4,4′-DDE .......................
GC/MS ...........
GC ..................
625
608
6410 B ..................
6630 B & C ..........
6410 B–00.
...............................
D3086–90, ............
D5812–96(02) ......
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 8
20. 4,4′-DDT .......................
GC/MS ...........
GC ..................
625
608
6410 B ..................
6630 B & C ..........
6410 B–00.
...............................
D3086–90, ............
D5812–96(02) ......
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 8
21. Demeton-O ...................
GC/MS ...........
GC ..................
625
....................
6410 B ..................
...............................
6410 B–00.
...............................
...............................
22. Demeton-S ...................
GC ..................
....................
...............................
...............................
...............................
23. Diazinon .......................
GC ..................
....................
...............................
...............................
...............................
24. Dicamba .......................
25. Dichlofen-thion .............
GC ..................
GC ..................
....................
....................
...............................
...............................
...............................
...............................
...............................
...............................
26. Dichloran ......................
27. Dicofol ..........................
GC ..................
GC ..................
....................
....................
6630 B & C ..........
...............................
...............................
...............................
28. Dieldrin .........................
GC ..................
608
6630 B & C ..........
...............................
...............................
D3086–90, ............
D5812–96(02).
...............................
See footnote 3, p. 25; See footnote 6,
p. S51
See footnote 3, p. 25; See footnote 6,
p. S51
See footnote 3, p. 25; See footnote 4,
p. 27; See footnote 6, p. S51
See footnote 3, p. 115
See footnote 4, p. 27; See footnote 6,
p. S73
See footnote 3, p. 7
29. Dioxathion ....................
GC/MS ...........
GC ..................
625
....................
6410 B ..................
...............................
6410 B–00.
...............................
...............................
30. Disulfoton .....................
GC ..................
....................
...............................
...............................
...............................
31. Diuron ...........................
TLC ................
....................
...............................
...............................
...............................
32. Endosulfan I .................
GC ..................
608
6630 B & C ..........
...............................
D3086–90, ............
D5812–96(02) ......
33. Endosulfan II ................
GC/MS ...........
GC ..................
625 5
608
6410 B ..................
6630 B & C ..........
6410 B–00.
...............................
GC/MS ...........
GC ..................
GC/MS ...........
GC ..................
625 5
608
625
608
6410
6630
6410
6630
B ..................
C ..................
B ..................
B & C ..........
6410 B–00.
...............................
6410 B–00.
...............................
625 5
608
625
....................
6410 B ..................
...............................
37. Ethion ...........................
GC/MS ...........
GC ..................
GC/MS ...........
GC ..................
38. Fenuron ........................
TLC ................
39. Fenuron-TCA ................
40. Heptachlor ....................
See footnote 3, p. 94, See footnote 6,
p. S60
See footnote 4, p. 27; See footnote 6,
p. S73
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 8
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 8
See footnote 4, p. 27; See footnote 6,
p. S73
See footnote 3, p. 25; See footnote 6,
p. S51
See footnote 3, p. 104; See footnote 6,
p. S64
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 8
D3086–90, ............
D5812–96(02) ......
See footnote 3, p. 7; See footnote 8
...............................
See footnote 8
D3086–90, ............
D5812–96(02) ......
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 8
6410 B–00.
...............................
...............................
See footnote 8
...............................
...............................
...............................
....................
...............................
...............................
...............................
TLC ................
....................
...............................
...............................
...............................
41. Heptachlor epoxide ......
GC ..................
GC/MS ...........
GC ..................
GC/MS ...........
608
625
608
625
6630
6410
6630
6410
& C ..........
..................
& C ..........
..................
...............................
6410 B–00.
...............................
6410 B–00.
D3086–90, ............
D5812–96(02) ......
D3086–90, ............
D5812– 96(02) .....
42. Isodrin ...........................
GC ..................
....................
...............................
...............................
...............................
43. Linuron .........................
GC ..................
....................
...............................
...............................
...............................
44. Malathion ......................
GC ..................
....................
6630 C ..................
...............................
...............................
See footnote 4, p. 27; See footnote 6,
p. S73
See footnote 3, p. 104; See footnote 6,
p. S64
See footnote 3, p. 104; See footnote 6,
p. S64
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 8
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 6, p. S73; See
footnote 8
See footnote 4, p. 27; See footnote 6,
p. S73
See footnote 3, p. 104; See footnote 6,
p. S64
See footnote 3, p. 25; See footnote 4,
p. 27; See footnote 6, p. S51
34. Endosulfan Sulfate .......
35. Endrin ...........................
rwilkins on PROD1PC63 with RULES
36. Endrin aldehyde ...........
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11233
TABLE ID.—LIST OF APPROVED TEST PROCEDURES FOR PESTICIDES 1—Continued
Parameter
Method
EPA 2, 7
Standard Methods
18th, 19th, 20th Ed.
Standard Methods
Online
ASTM
Other
45. Methiocarb ....................
TLC ................
....................
...............................
...............................
...............................
46. Methoxy-chlor ...............
GC ..................
....................
6630 B & C ..........
...............................
47. Mexacar-bate ...............
TLC ................
....................
...............................
...............................
D3086–90,
D5812–96(02).
...............................
48. Mirex .............................
GC ..................
....................
6630 B & C ..........
...............................
...............................
49. Monuron .......................
TLC ................
....................
...............................
...............................
...............................
50. Monuron-TCA ...............
TLC ................
....................
...............................
...............................
...............................
51. Nuburon ........................
TLC ................
....................
...............................
...............................
...............................
52. Parathion methyl ..........
GC ..................
....................
6630 C ..................
...............................
...............................
53. Parathion ethyl .............
GC ..................
....................
6630 C ..................
...............................
...............................
54. PCNB ...........................
55. Perthane .......................
GC ..................
GC ..................
....................
....................
6630 B & C ..........
...............................
...............................
...............................
56. Prometon ......................
GC ..................
....................
...............................
...............................
...............................
D3086–90,
D5812–96(02).
...............................
See footnote 3, p. 94; See footnote 6,
p. S60
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 8
See footnote 3, p. 94; See footnote 6,
p.S60
See footnote 3, p. 7; See footnote 4, p.
27
See footnote 3, p. 104; See footnote 6,
p. S64
See footnote 3, p. 104; See footnote 6,
p. S64
See footnote 3, p. 104; See footnote 6,
p. S64
See footnote 3, p. 25; See footnote 4,
p. 27
See footnote 3, p. 25; See footnote 4,
p. 27
See footnote 3, p. 7
See footnote 4, p. 27
57. Prometryn .....................
GC ..................
....................
...............................
...............................
...............................
58. Propazine .....................
GC ..................
....................
...............................
...............................
...............................
59. Propham .......................
TLC ................
....................
...............................
...............................
...............................
60. Propoxur .......................
TLC ................
....................
...............................
...............................
...............................
61. Secbumeton .................
TLC ................
....................
...............................
...............................
...............................
62. Siduron .........................
TLC ................
....................
...............................
...............................
...............................
63. Simazine .......................
GC ..................
....................
...............................
...............................
...............................
64. Strobane .......................
65. Swep ............................
GC ..................
TLC ................
....................
....................
6630 B & C ..........
...............................
...............................
...............................
...............................
...............................
66. 2,4,5–T .........................
GC ..................
....................
6640 B ..................
...............................
...............................
67. 2,4,5–TP (Silvex) ..........
GC ..................
....................
6640 B ..................
...............................
...............................
68. Terbuthylazine ..............
GC ..................
....................
...............................
...............................
...............................
69. Toxaphene ...................
GC ..................
608
6630 B & C ..........
...............................
D3086–90,
D5812–96(02).
See footnote 3, p. 83; See footnote 6,
p. S68; See footnote 9
See footnote 3, p. 83; See footnote 6,
p. S68; See footnote 9
See footnote 3, p. 83; See footnote 6,
p. S68; See footnote 9
See footnote 3, p. 104; See footnote 6,
p. S64
See footnote 3, p. 94; See footnote 6,
p. S60
See footnote 3, p. 83; See footnote 6,
p. S68
See footnote 3, p. 104; See footnote 6,
p. S64
See footnote 3, p. 83; See footnote 6,
p. S68; See footnote 9
See footnote 3, p. 7
See footnote 3, p. 104; See footnote 6,
p. S64
See footnote 3, p. 115; See footnote 4,
p. 40
See footnote 3, p. 115; See footnote 4,
p. 40
See footnote 3, p. 83; See footnote 6,
p. S68
See footnote 3, p. 7; See footnote 4, p.
27; See footnote 8
70. Trifluralin .......................
GC/MS ...........
GC ..................
625
....................
6410 B ..................
6630 B ..................
6410 B–00.
...............................
...............................
See footnote 3, p. 7; See footnote 9
1 Pesticides
are listed in this table by common name for the convenience of the reader. Additional pesticides may be found under Table IC, where entries are listed by chemical name.
2 The full text of Methods 608 and 625 are given at Appendix A, ‘‘Test Procedures for Analysis of Organic Pollutants,’’ of this Part 136. The standardized test procedure to be used to determine the method detection limit (MDL) for these test procedures is given at Appendix B, ‘‘Definition and Procedure for the Determination of the Method Detection Limit,’’ of this Part 136.
3 ‘‘Methods for Benzidine, Chlorinated Organic Compounds, Pentachlorophenol and Pesticides in Water and Wastewater,’’ U.S. Environmental Protection Agency, September 1978. This
EPA publication includes thin-layer chromatography (TLC) methods.
4‘‘Methods for Analysis of Organic Substances in Water and Fluvial Sediments,’’ Techniques of Water-Resources Investigations of the U.S. Geological Survey, Book 5, Chapter A3 (1987).
5 The method may be extended to include a-BHC, g-BHC, endosulfan I, endosulfan II, and endrin. However, when they are known to exist, Method 608 is the preferred method.
6 ‘‘Selected Analytical Methods Approved and Cited by the United States Environmental Protection Agency.’’ Supplement to the Fifteenth Edition of Standard Methods for the Examination of
Water and Wastewater (1981).
7 Each analyst must make an initial, one-time, demonstration of their ability to generate acceptable precision and accuracy with Methods 608 and 625 (See Appendix A of this Part 136) in
accordance with procedures given in Section 8.2 of each of these methods. Additionally, each laboratory, on an on-going basis, must spike and analyze 10% of all samples analyzed with
Method 608 or 5% of all samples analyzed with Method 625 to monitor and evaluate laboratory data quality in accordance with Sections 8.3 and 8.4 of these methods. When the recovery of
any parameter falls outside the warning limits, the analytical results for that parameter in the unspiked sample are suspect. The results should be reported, but cannot be used to demonstrate regulatory compliance. These quality control requirements also apply to the Standard Methods, ASTM Methods, and other methods cited.
8 ‘‘Organochlorine Pesticides and PCBs in Wastewater Using EmporeTM Disk’’, 3M Corporation, Revised 10/28/94.
9 USGS Method 0–3106–93 from ‘‘Methods of Analysis by the U.S. Geological Survey National Water Quality Laboratory—Determination of Triazine and Other Nitrogen-containing Compounds by Gas Chromatography with Nitrogen Phosphorus Detectors’’ U.S. Geological Survey Open File Report 94–37.
TABLE IE.—LIST OF APPROVED RADIOLOGIC TEST TEST PROCEDURES
Reference (method number or page)
Parameter and units
Method
rwilkins on PROD1PC63 with RULES
EPA 1
1. Alpha-Total, pCi per
liter.
2. Alpha-Counting
error, pCi per liter.
3. Beta-Total, pCi per
liter.
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Proportional or scintillation counter.
Proportional counter ...
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20th Ed.
Standard Methods Online
ASTM
900.0 ...........
7110 B ................
7110 B–00 ..........
D1943–90, 96 ....
pp. 75 and 78 3
Appendix B ..
7110 B ................
7110 B–00 ..........
D1943–90, 96 ....
p. 79
900.0 ...........
7110 B ................
7110 B–00 ..........
D1890–90, 96 ....
pp. 75 and 78 3
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11234
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
TABLE IE.—LIST OF APPROVED RADIOLOGIC TEST TEST PROCEDURES—Continued
Reference (method number or page)
Parameter and units
EPA 1
Standard Methods 18th, 19th,
20th Ed.
Standard Methods Online
ASTM
Proportional counter ...
Appendix B ..
7110 B ................
7110 B–00 ..........
D1890–90, 96 .....
Proportional counter ...
903.0 ...........
7500-Ra B ..........
7500-Ra B–01 ....
D2460–90, 97 .....
Scintillation counter ....
4. Beta-Counting error,
pCi.
5. (a) Radium Total
pCi per liter.
(b) Ra, pCi per liter ....
Method
903.1 ...........
7500-Ra C ..........
7500-Ra C–01 ....
D3454–91, 97 .....
USGS 2
p. 79
p. 81
1 Prescribed
Procedures for Measurement of Radioactivity in Drinking Water, EPA–600/4–80–032 (1980), U.S. Environmental Protection Agency, August 1980.
2 Fishman, M. J. and Brown, Eugene, ‘‘Selected Methods of the U.S. Geological Survey of Analysis of Wastewaters,’’ U.S. Geological Survey,
Open-File Report 76–177 (1976).
3 The method found on p. 75 measures only the dissolved portion while the method on p. 78 measures only the suspended portion. Therefore,
the two results must be added to obtain the ‘‘total.’’
*
*
*
*
*
TABLE IG.—TEST METHODS FOR PESTICIDE ACTIVE INGREDIENTS
rwilkins on PROD1PC63 with RULES
EPA Survey
Code
Pesticide name
8 ..................
12 ................
16 ................
17 ................
22 ................
25 ................
26 ................
27 ................
30 ................
31 ................
35 ................
39 ................
41 ................
45 ................
52 ................
53 ................
54 ................
55 ................
58 ................
60 ................
62 ................
68 ................
69 ................
69 ................
70 ................
73 ................
75 ................
76 ................
80 ................
82 ................
84 ................
86 ................
90 ................
103 ..............
107 ..............
110 ..............
112 ..............
113 ..............
118 ..............
119 ..............
123 ..............
124 ..............
125 ..............
126 ..............
127 ..............
132 ..............
133 ..............
138 ..............
140 ..............
144 ..............
148 ..............
150 ..............
154 ..............
156 ..............
Triadimefon ...........................................................................................................................
Dichlorvos ..............................................................................................................................
2,4–D; 2,4–D Salts and Esters [2,4–Dichloro-phenoxyacetic acid] ......................................
2,4–DB; 2,4–DB Salts and Esters [2,4–Dichlorophenoxybutyric acid] .................................
Mevinphos .............................................................................................................................
Cyanazine .............................................................................................................................
Propachlor .............................................................................................................................
MCPA; MCPA Salts and Esters [2–Methyl-4-chlorophenoxyacetic acid] .............................
Dichlorprop; Dichlorprop Salts and Esters [2–(2,4–Dichlorophenoxy) propionic acid] .........
MCPP; MCPP Salts and Esters [2–(2–Methyl-4-chlorophenoxy) propionic acid] ................
TCMTB [2–(Thiocyanomethylthio) benzo-thiazole] ...............................................................
Pronamide .............................................................................................................................
Propanil .................................................................................................................................
Metribuzin ..............................................................................................................................
Acephate ...............................................................................................................................
Acifluorfen .............................................................................................................................
Alachlor .................................................................................................................................
Aldicarb .................................................................................................................................
Ametryn .................................................................................................................................
Atrazine .................................................................................................................................
Benomyl ................................................................................................................................
Bromacil; Bromacil Salts and Esters ....................................................................................
Bromoxynil .............................................................................................................................
Bromoxynil octanoate ............................................................................................................
Butachlor ...............................................................................................................................
Captafol .................................................................................................................................
Carbaryl [Sevin] .....................................................................................................................
Carbofuran ............................................................................................................................
Chloroneb ..............................................................................................................................
Chlorothalonil ........................................................................................................................
Stirofos ..................................................................................................................................
Chlorpyrifos ...........................................................................................................................
Fenvalerate ...........................................................................................................................
Diazinon ................................................................................................................................
Parathion methyl ...................................................................................................................
DCPA [Dimethyl 2,3,5,6-tetrachloro-terephthalate] ...............................................................
Dinoseb .................................................................................................................................
Dioxathion .............................................................................................................................
Nabonate [Disodium cyanodithio-imidocarbonate] ...............................................................
Diuron ....................................................................................................................................
Endothall ...............................................................................................................................
Endrin ....................................................................................................................................
Ethalfluralin ............................................................................................................................
Ethion ....................................................................................................................................
Ethoprop ................................................................................................................................
Fenarimol ..............................................................................................................................
Fenthion ................................................................................................................................
Glyphosate [N(Phosphonomethyl) glycine] ...........................................................................
Heptachlor .............................................................................................................................
Isopropalin .............................................................................................................................
Linuron ..................................................................................................................................
Malathion ...............................................................................................................................
Methamidophos .....................................................................................................................
Methomyl ...............................................................................................................................
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43121–43–3
62–73–7
94–75–7
94–82–6
7786–34–7
21725–46–2
1918–16–7
94–74–6
120–36–5
93–65–2
21564–17–0
23950–58–5
709–98–8
21087–64–9
30560–19–1
50594–66–6
15972–60–8
116–06–3
834–12–8
1912–24–9
17804–35–2
314–40–9
1689–84–5
1689–99–2
23184–66–9
2425–06–1
63–25–2
1563–66–2
2675–77–6
1897–45–6
961–11–5
2921–88–2
51630–58–1
333–41–5
298–00–0
1861–32–1
88–85–7
78–34–2
138–93–2
330–54–1
145–73–3
72–20–8
55283–68–6
563–12–2
13194–48–4
60168–88–9
55–38–9
1071–83–6
76–44–8
33820–53–0
330–55–2
121–75–5
10265–92–6
16752–77–5
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1657/507/622/525.1
1658/515.1/615/515.2/555
1658/515.1/615/515.2/555
1657/507/622/525.1
629/507
1656/508/608.1/525.1
1658/615/555
1658/515.1/615/515.2/555
1658/615/555
637
525.1/507/633.1
632.1/1656
507/633/525.1/1656
1656/1657
515.1/515.2/555
505/507/645/525.1/1656
531.1
507/619/525.1
505/507/619/525.1/1656
631
507/633/525.1/1656
1625/1661
1656
507/645/525.1/1656
1656
531.1/632/553
531.1/632
1656/508/608.1/525.1
508/608.2/525.1/1656
1657/507/622/525.1
1657/508/622
1660
1657/507/614/622/525.1
1657/614/622
508/608.2/525.1/515.1/515.2/1656
1658/515.1/615/515.2/555
1657/614.1
630.1
632/553
548/548.1
1656/505/508/608/617/525.1
1656/627 See footnote 1
1657/614/614.1
1657/507/622/525.1
507/633.1/525.1/1656
1657/622
547
1656/505/508/608/617/525.1
1656/627
553/632
1657/614
1657
531.1/632
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11235
TABLE IG.—TEST METHODS FOR PESTICIDE ACTIVE INGREDIENTS—Continued
EPA Survey
Code
158
172
173
175
178
182
183
185
186
192
197
203
204
205
206
208
212
218
219
220
223
224
226
230
232
236
239
241
243
252
254
255
256
257
259
262
263
264
268
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
..............
1 Monitor
Pesticide name
Methoxychlor .........................................................................................................................
Nabam ...................................................................................................................................
Naled .....................................................................................................................................
Norflurazon ............................................................................................................................
Benfluralin .............................................................................................................................
Fensulfothion .........................................................................................................................
Disulfoton ..............................................................................................................................
Phosmet ................................................................................................................................
Azinphos Methyl ....................................................................................................................
Organo-tin pesticides ............................................................................................................
Bolstar ...................................................................................................................................
Parathion ...............................................................................................................................
Pendimethalin ........................................................................................................................
Pentachloronitrobenzene ......................................................................................................
Pentachlorophenol ................................................................................................................
Permethrin .............................................................................................................................
Phorate ..................................................................................................................................
Busan 85 [Potassium dimethyldithiocarbamate] ...................................................................
Busan 40 [Potassium N-hydroxymethyl-N-methyldithiocarbamate] ......................................
KN Methyl [Potassium N-methyl-dithiocarbamate] ...............................................................
Prometon ...............................................................................................................................
Prometryn ..............................................................................................................................
Propazine ..............................................................................................................................
Pyrethrin I ..............................................................................................................................
Pyrethrin II .............................................................................................................................
DEF [S,S,S–Tributyl phosphorotrithioate] .............................................................................
Simazine ................................................................................................................................
Carbam-S [Sodium dimethyldithiocarbanate] .......................................................................
Vapam [Sodium methyldithiocarbamate] ..............................................................................
Tebuthiuron ...........................................................................................................................
Terbacil ..................................................................................................................................
Terbufos ................................................................................................................................
Terbuthylazine .......................................................................................................................
Terbutryn ...............................................................................................................................
Dazomet ................................................................................................................................
Toxaphene ............................................................................................................................
Merphos [Tributyl phosphorotrithioate] .................................................................................
Trifluralin ................................................................................................................................
Ziram [Zinc dimethyldithiocarbamate] ...................................................................................
EPA Analytical Method No.(s)
72–43–5
142–59–6
300–76–5
27314–13–2
1861–40–1
115–90–2
298–04–4
732–11–6
86–50–0
12379–54–3
35400–43–2
56–38–2
40487–42–1
82–68–8
87–86–5
52645–53–1
298–02–2
128–03–0
51026–28–9
137–41–7
1610–18–0
7287–19–6
139–40–2
121–21–1
121–29–9
78–48–8
122–34–9
128–04–1
137–42–8
34014–18–1
5902–51–2
13071–79–9
5915–41–3
886–50–0
533–74–4
8001–35–2
150–50–5
1582–09–8
137–30–4
1656/505/508/608.2/617/525.1
630/630.1
1657/622
507/645/525.1/1656
11656/1627
1657/622
1657/507/614/622/525.1
1657/622.1
1657/614/622
Ind-01/200.7/200.9
1657/622
1657/614
1656
1656/608.1/617
625/1625/515.2/555/515.1/ 525.1
608.2/508/525.1/1656/1660
1657/622
630/630.1
630/630.1
630/630.1
507/619/525.1
507/619/525.1
507/619/525.1/1656
1660
1660
1657
505/507/619/525.1/1656
630/630.1
630/630.1
507/525.1
507/633/525.1/1656
1657/507/614.1/525.1
619/1656
507/619/525.1
630/630.1/1659
1656/505/508/608/617/525.1
1657/507/525.1/622
1656/508/617/627/525.1
630/630.1
and report as total Trifluralin.
(b) * * *
References, Sources, Costs, and Table
Citations
*
rwilkins on PROD1PC63 with RULES
CAS No.
*
*
*
*
(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 are available through
the Standard Methods Web site (https://
www.standardmethods.org). Tables IA,
IB, IC, ID, IE.
*
*
*
*
*
(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, and IE.
*
*
*
*
*
VerDate Aug<31>2005
18:34 Mar 09, 2007
Jkt 211001
(17) AOAC-International. Official
Methods of Analysis of AOACInternational, 16th Edition, (1995).
Available from: AOAC-International,
481 North Frederick Avenue, Suite 500,
Gaithersburg, MD 20877. Table IB, See
footnote 3.
*
*
*
*
*
(63) Waters Corporation. Method
D6508, Rev. 2, ‘‘Test Method for
Determination of Dissolved Inorganic
Anions in Aqueous Matrices Using
Capillary Ion Electrophoresis and
Chromate Electrolyte,’’ available from
Waters Corp, 34 Maple Street, Milford,
MA 01757, Telephone: 508/482–2131,
Fax: 508/482–3625, Table IB, See
footnote 54.
(64) Kelada-01, ‘‘Kelada Automated
Test Methods for Total Cyanide, Acid
Dissociable Cyanide, and Thiocyanate,’’
EPA 821–B–01–009 Revision 1.2,
August 2001 is available from National
Technical Information Service (NTIS),
5285 Port Royal Road, Springfield, VA
22161 [Order Number PB 2001–108275].
Telephone: 800–553–6847. Table IB, See
footnote 55.
(65) QuikChem Method 10–204–00–
1–X, ‘‘Digestion and Distillation of Total
PO 00000
Frm 00037
Fmt 4701
Sfmt 4700
Cyanide in Drinking and Wastewaters
using MICRO DIST and Determination
of Cyanide by Flow Injection Analysis’’
Revision 2.2, March 2005 is available
from Lachat Instruments 6645 W. Mill
Road, Milwaukee, WI 53218, Telephone:
414–358–4200. Table IB, See footnote
56.
(66) ‘‘Methods for the Determination
of Metals in Environmental Samples,’’
Supplement I, National Exposure Risk
Laboratory-Cincinnati (NERL–CI), EPA/
600/R–94/111, May 1994; and ‘‘Methods
for the Determination of Inorganic
Substances in Environmental Samples,’’
NERL–CI, EPA/600/R–93/100, August,
1993 are available from National
Technical Information Service (NTIS),
5285 Port Royal Road, Springfield, VA
22161. Telephone: 800–553–6847. Table
IB.
(67) ‘‘Determination of Inorganic Ions
in Drinking Water by Ion
Chromatography,’’ Rev. 1.0, 1997 is
available from from https://www.epa.gov/
safetwater/methods/met300.pdf. Table
IB.
(68) Table IG Methods are available in
‘‘Methods For The Determination of
Nonconventional Pesticides In
E:\FR\FM\12MRR2.SGM
12MRR2
11236
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
Municipal and Industrial Wastewater,
Volume I,’’ EPA 821–R–93–010A,
August 1993 Revision I, and ‘‘Methods
For The Determination of
Nonconventional Pesticides In
Municipal and Industrial Wastewater,
Volume II,’’ EPA 821–R–93–010B
(August 1993) are available from
National Technical Information Service
(NTIS), 5285 Port Royal Road,
Springfield, VA 22161. Telephone: 800–
553–6847.
(69) Method 245.7, Rev. 2.0, ‘‘Mercury
in Water by Cold Vapor Atomic
Fluorescence Spectrometry,’’ February
2005, EPA–821–R–05–001, available
from the U.S. EPA Sample Control
Center (operated by CSC), 6101
Stevenson Avenue, Alexandria, VA
22304, Telephone: 703–461–8056. Table
IB, See footnote 59.
(c) Under certain circumstances, the
Regional Administrator or the Director
in the Region or State where the
discharge will occur may determine for
a particular discharge that additional
parameters or pollutants must be
reported. Under such circumstances,
additional test procedures for analysis
of pollutants may be specified by the
Regional Administrator, or the Director
upon recommendation of the Alternate
Test Procedure Program Coordinator,
Washington, DC.
(d) Under certain circumstances, the
Administrator may approve additional
alternate test procedures for nationwide
use, upon recommendation by the
Alternate Test Procedure Program
Coordinator, Washington, DC.
(e) Sample preservation procedures,
container materials, and maximum
allowable holding times for parameters
are cited in Tables IA, IB, IC, ID, IE, IF,
and IG 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.
TABLE II.—REQUIRED CONTAINERS, PRESERVATION TECHNIQUES, AND HOLDING TIMES
Parameter number/name
Container 1
Table lA—Bacterial Tests:
1–5. Coliform, total, fecal, and E. coli ..........................................................................
PA, G .........................
6. Fecal streptococci .....................................................................................................
PA, G .........................
7. Enterococci ...............................................................................................................
PA, G .........................
Table lA—Protozoan Tests:
8. Cryptosporidium ........................................................................................................
9. Giardia ......................................................................................................................
Table lA—Aquatic Toxicity Tests:
10–13. Toxicity, acute and chronic ...............................................................................
Table lB—Inorganic Tests:
1. Acidity .......................................................................................................................
2. Alkalinity ....................................................................................................................
4. Ammonia ...................................................................................................................
6 hours
LDPE; field filtration ...
LDPE; field filtration ...
0–8 °C .............
0–8 °C .............
96 hours 21
96 hours 21
P, FP, G ....................
Cool, ≤6 °C 16 ..
36 hours
P, FP, G ....................
P, FP, G ....................
P, FP, G ....................
FP, G ....................
FP, or Quartz ........
FP, G ....................
FP G .....................
FP, G ....................
16. Chloride ...................................................................................................................
17. Chlorine, total residual ............................................................................................
21. Color .......................................................................................................................
23–24. Cyanide, total or available (or CATC) ..............................................................
P,
P,
P,
P,
FP, G ....................
G ...........................
FP, G ....................
FP, G ....................
25. Fluoride ...................................................................................................................
27. Hardness .................................................................................................................
P ................................
P, FP, G ....................
28. Hydrogen ion (pH) ..................................................................................................
31, 43. Kjeldahl and organic N .....................................................................................
rwilkins on PROD1PC63 with RULES
P,
P,
P,
P,
P,
P, FP, G ....................
P, FP, G ....................
Table IB—Metals: 7
18. Chromium VI ...........................................................................................................
P, FP, G ....................
35. Mercury (CVAA) ......................................................................................................
P, FP, G ....................
18:34 Mar 09, 2007
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Maximum holding time 4
Cool, <10 °C,
0.0008%
Na2S2O3 5.
Cool, <10 °C,
0.0008%
Na2S2O3 5.
Cool, <10 °C,
0.0008%
Na2S2O3 5.
9. Biochemical oxygen demand ....................................................................................
10. Boron ......................................................................................................................
11. Bromide ...................................................................................................................
14. Biochemical oxygen demand, carbonaceous .........................................................
15. Chemical oxygen demand ......................................................................................
VerDate Aug<31>2005
Preservation 2,3
Sfmt 4700
°C 18
Cool, ≤6
..
Cool, ≤6 °C 18 ..
18,
Cool, ≤6 °C
H2SO4 to
pH<2.
Cool, ≤6 °C 18 ..
HNO3 to pH<2
None required
Cool, ≤6 °C 18 ..
Cool, ≤6 °C 18,
H2SO4 to
pH<2.
None required
None required
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
Cool, ≤6 °C 18,
H2SO4 to
pH<2.
Cool, ≤6 °C 18,
pH = 9.3–
9.7 20.
HNO3 to pH<2
E:\FR\FM\12MRR2.SGM
12MRR2
6 hours
6 hours
14 days
14 days
28 days
48 hours
6 months
28 days
48 hours
28 days
28 days
Analyze within 15 minutes
48 hours
14 days
28 days
6 months
Analyze within 15 minutes
28 days
28 days
28 days
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
11237
TABLE II.—REQUIRED CONTAINERS, PRESERVATION TECHNIQUES, AND HOLDING TIMES—Continued
Container 1
Parameter number/name
35. Mercury (CVAFS) ...................................................................................................
FP, G; and FP-lined
cap 17.
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.
P, FP, G ....................
38. Nitrate .....................................................................................................................
39. Nitrate-nitrite ...........................................................................................................
P, FP, G ....................
P, FP, G ....................
40. Nitrite .......................................................................................................................
41. Oil and grease ........................................................................................................
P, FP, G ....................
G ................................
42. Organic Carbon ......................................................................................................
P, FP, G ....................
44. Orthophosphate ......................................................................................................
P, FP, G ....................
46. Oxygen, Dissolved Probe .......................................................................................
47. Winkler ....................................................................................................................
G, Bottle and top .......
G, Bottle and top .......
48. Phenols ...................................................................................................................
G ................................
49. Phosphorous (elemental) ........................................................................................
50. Phosphorous, total ..................................................................................................
G ................................
P, FP, G ....................
53.
54.
55.
56.
57.
61.
64.
65.
66.
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 ....................
Residue, total ..........................................................................................................
Residue, Filterable ..................................................................................................
Residue, Nonfilterable (TSS) ..................................................................................
Residue, Settleable .................................................................................................
Residue, Volatile .....................................................................................................
Silica .......................................................................................................................
Specific conductance ..............................................................................................
Sulfate .....................................................................................................................
Sulfide .....................................................................................................................
67. Sulfite ......................................................................................................................
68. Surfactants ..............................................................................................................
69. Temperature ...........................................................................................................
73. Turbidity ..................................................................................................................
Table lC—Organic Tests 8
13, 18–20, 22, 24–28, 34–37, 39–43, 45–47, 56, 76, 104, 105, 108–111, 113.
Purgeable Halocarbons.
P,
P,
P,
P,
FP,
FP,
FP,
FP,
G
G
G
G
....................
....................
....................
....................
G, FP-lined septum ...
G, FP-lined septum ...
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 .........
7, 38. Benzidines 11, 12 ..................................................................................................
G, FP-lined cap .........
14, 17, 48, 50–52. Phthalate esters 11 .........................................................................
G, FP-lined cap .........
82–84. Nitrosamines11 14 ..............................................................................................
rwilkins on PROD1PC63 with RULES
6, 57, 106. Purgeable aromatic hydrocarbons .............................................................
G, FP-lined cap .........
88–94. PCBs 11 .............................................................................................................
G, FP-lined cap .........
54, 55, 75, 79. Nitroaromatics and isophorone 11 ........................................................
G, FP-lined cap .........
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18:34 Mar 09, 2007
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Frm 00039
Fmt 4701
Sfmt 4700
Preservation 2,3
5 mL/L 12N
HCl or 5 mL/
L BrCl 17.
HNO3 to pH<2,
or at least 24
hours prior to
analysis 19.
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 ..
None required
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
Cool, ≤6 °C 18 ..
None required
Cool, ≤6 °C 18
Cool, ≤6 °C 18,
0.008%
Na2S2O3 5.
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.
Cool, ≤6 °C 18,
0.008%
Na2S2O3 5.
Cool, ≤6 °C 18 ..
Cool, ≤6 °C 18,
store in dark,
0.008%
Na2S2O35.
Cool, ≤6 °C 18 ..
Cool, ≤6 °C 18,
store in dark,
0.008%
Na2S2O35.
E:\FR\FM\12MRR2.SGM
12MRR2
Maximum holding time 4
90 days 17
6 months
48 hours
28 days
48 hours
28 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
14 days
14 days 9
14 days 10
7 days until extraction, 40 days
after extraction
7 days until extraction 13
7 days
after
7 days
after
until extraction, 40 days
extraction
until extraction, 40 days
extraction
1 year until extraction, 1 year
after extraction
7 days until extraction, 40 days
after extraction
11238
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
TABLE II.—REQUIRED CONTAINERS, PRESERVATION TECHNIQUES, AND HOLDING TIMES—Continued
Container 1
Preservation 2,3
Maximum holding time 4
1, 2, 5, 8–12, 32, 33, 58, 59, 74, 78, 99, 101. Polynuclear aromatic hydrocarbons 11
G, FP-lined cap .........
7 days until extraction, 40 days
after extraction
15, 16, 21, 31, 87. Haloethers 11 ..................................................................................
G, FP-lined cap .........
29, 35-37, 63-65, 107. Chlorinated hydrocarbons 11 ....................................................
G, FP-lined cap .........
Cool, ≤6 °C 18,
store in dark,
0.008%
Na2S2O35.
Cool, ≤6 °C 18,
0.008%
Na2S2O35.
Cool, ≤6 °C 18 ..
60-62, 66-72, 85, 86, 95-97, 102, 103. CDDs/CDFs 11.
Aqueous Samples: Field and Lab Preservation ....................................................
G ................................
1 year
Solids and Mixed-Phase Samples: Field Preservation .........................................
Tissue Samples: Field Preservation ......................................................................
Solids, Mixed-Phase, and Tissue Samples: Lab Preservation .............................
G ................................
G ................................
G ................................
Cool, ≤6 °C 18,
0.008%
Na2S2O35,
pH<9.
Cool, ≤6 °C 18 ..
Cool, ≤6 °C 18
Freeze, ≤¥10
°C.
Table lD—Pesticides Tests:
1–70. Pesticides 11 ........................................................................................................
G, FP-lined cap .........
Cool, ≤6 °C 18,
pH 5–9 15.
7 days until extraction, 40 days
after extraction
Table lE—Radiological Tests:
1–5. Alpha, beta, and radium .......................................................................................
P, FP, G ....................
HNO3 to pH<2
6 months
Parameter number/name
7 days until extraction, 40 days
after extraction
7 days
24 hours
1 year
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 with in 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).
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 ), ascorbic acid, sodium arsenite (NaAsO ), or
2 2 3
2
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 well-ventilated 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 well-ventilated 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 form 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 (g 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.
1 ‘‘P’’
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after extraction
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(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.
(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 24hour 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.
8. Section 136.4 is amended by
revising the first sentence of paragraph
(d) introductory text to read as follows:
I
§ 136.4 Application for alternate test
procedures.
*
*
*
*
*
(d) An application for approval of an
alternate test procedure for nationwide
use may be made by letter in triplicate
to the Alternate Test Procedure Program
Coordinator, Office of Science and
Technology (4303), Office of Water, U.S.
Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460. * * *
*
*
*
*
*
I 9. Section 136.5 is amended as
follows:
I a. In paragraph (b) by revising the last
sentence.
I b. By revising paragraph (c).
I c. In paragraph (d) by revising the
second and third sentences.
I d. By revising paragraphs (e)(1) and
(e)(2).
§ 136.5 Approval of alternate test
procedures.
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*
*
*
*
(b) * * * Where the Director
recommends rejection of the application
for scientific and technical reasons
which he provides, the Regional
Administrator shall deny the
application and shall forward this
decision to the Director of the State
Permit Program and to the Alternate
Test Procedure Program Coordinator,
Office of Science and Technology
(4303), Office of Water, U.S.
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Environmental Protection Agency, 1200
Pennsylvania Ave., NW., Washington,
DC 20460.
(c) Before approving any application
for an alternate test procedure proposed
by the responsible person or firm
making the discharge, the Regional
Administrator shall forward a copy of
the application to the Alternate Test
Procedure Program Coordinator, Office
of Science and Technology (4303),
Office of Water, U.S. Environmental
Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460.
(d) * * * Prior to the expiration of
such ninety day period, a
recommendation providing the
scientific and other technical basis for
acceptance or rejection will be
forwarded to the Regional Administrator
by the Alternate Test Procedure Program
Coordinator, Washington, DC. A copy of
all approval and rejection notifications
will be forwarded to the Alternate Test
Procedure Program Coordinator, Office
of Science and Technology (4303),
Office of Water, U.S. Environmental
Protection Agency, 1200 Pennsylvania
Ave., NW., Washington, DC 20460, for
the purposes of national coordination.
(e) Approval for nationwide use. (1)
As expeditiously as is practicable after
receipt by the Alternate Test Procedure
Program Coordinator, Washington, DC,
of an application for an alternate test
procedure for nationwide use, the
Alternate Test Procedure Program
Coordinator, Washington, DC, shall
notify the applicant in writing whether
the application is complete. If the
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application is incomplete, the applicant
shall be informed of the information
necessary to make the application
complete.
(2) As expeditiously as is practicable
after receipt of a complete package, the
Alternate Test Procedure Program
Coordinator shall perform any analysis
necessary to determine whether the
alternate test procedure satisfies the
applicable requirements of this part, and
the Alternate Test Procedure Program
Coordinator shall recommend to the
Administrator that he/she approve or
reject the application and shall also
notify the application of the
recommendation.
*
*
*
*
*
I 10. Section 136.6 is added to Part 136
to read as follows:
§ 136.6 Method Modifications and
Analytical Requirements.
(a) Definitions of terms used in this
Section.
(1) Analyst means the person or
laboratory using a test procedure
(analytical method) in this Part.
(2) Chemistry of the Method means
the reagents and reactions used in a test
procedure that allow determination of
the analyte(s) of interest in an
environmental sample.
(3) Determinative Technique means
the way in which an analyte is
identified and quantified (e.g.,
colorimetry, mass spectrometry).
(4) Equivalent Performance means
that the modified method produces
results that meet the QC acceptance
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criteria of the approved method at this
part.
(5) Method-defined Analyte means an
analyte defined solely by the method
used to determine the analyte. Such an
analyte may be a physical parameter, a
parameter that is not a specific
chemical, or a parameter that may be
comprised of a number of substances.
Examples of such analytes include
temperature, oil and grease, total
suspended solids, total phenolics,
turbidity, chemical oxygen demand, and
biochemical oxygen demand.
(6) QC means ‘‘quality control.’’
(b) Method Modifications.
(1) Allowable Changes. Except as set
forth in paragraph (b)(3) of this section,
an analyst may modify an approved test
procedure (analytical method) provided
that the chemistry of the method or the
determinative technique is not changed,
and provided that the requirements of
paragraph (b)(2) of this section are met.
(i) Potentially acceptable
modifications regardless of current
method performance include changes
between automated and manual discrete
instrumentation; changes in the
calibration range (provided that the
modified range covers any relevant
regulatory limit); changes in equipment
such as using similar equipment from a
vendor other than that mentioned in the
method (e.g., a purge-and-trap device
from OIA rather than Tekmar), changes
in equipment operating parameters such
as changing the monitoring wavelength
of a colorimeter or modifying the
temperature program for a specific GC
column; changes to chromatographic
columns (treated in greater detail in
paragraph (d) of this section); and
increases in purge-and-trap sample
volumes (provided specifications in
paragraph (e) of this section are met).
The changes are only allowed provided
that all the requirements of paragraph
(b)(2) of this section are met.
(ii) If the characteristics of a
wastewater matrix prevent efficient
recovery of organic pollutants and
prevent the method from meeting QC
requirements, the analyst may attempt
to resolve the issue by using salts as
specified in Guidance on Evaluation,
Resolution, and Documentation of
Analytical Problems Associated with
Compliance Monitoring (EPA 821–B–
93–001, June 1993), provided that such
salts do not react with or introduce the
target pollutant into the sample (as
evidenced by the analysis of method
blanks, laboratory control samples, and
spiked samples that also contain such
salts) and that all requirements of
paragraph (b)(2) of this section are met.
Chlorinated samples must be
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dechlorinated prior to the addition of
such salts.
(iii) If the characteristics of a
wastewater matrix result in poor sample
dispersion or reagent deposition on
equipment and prevents the analyst
from meeting QC requirements, the
analysts may attempt to resolve the
issue by adding an inert surfactant (i.e.
a surfactant that will not affect the
chemistry of the method), which may
include Brij-35 or sodium dodecyl
sulfate (SDS), provided that such
surfactant does not react with or
introduce the target pollutant into the
sample (as evidenced by the analysis of
method blanks, laboratory control
samples, and spiked samples that also
contain such surfactant) and that all
requirements of paragraph (b)(2) of this
section are met. Chlorinated samples
must be dechlorinated prior to the
addition of such surfactant.
(2) Requirements. A modified method
must produce equivalent performance to
the approved methods for the analyte(s)
of interest, and the equivalent
performance must be documented.
(i) Requirements for Establishing
Equivalent Performance
(A) If the approved method contains
QC tests and QC acceptance criteria, the
modified method must use these QC
tests and the modified method must
meet the QC acceptance criteria. The
Analyst may only rely on QC tests and
QC acceptance criteria in a method if it
includes wastewater matrix QC tests
and QC acceptance criteria (e.g., as
matrix spikes) and both initial (start-up)
and ongoing QC tests and QC
acceptance criteria.
(B) If the approved method does not
contain QC tests and QC acceptance
criteria, or if the QC tests and QC
acceptance criteria in the method do not
meet the requirements of paragraph
(b)(2)(i)(A) of this section, the analyst
must employ QC tests specified in
Protocol for EPA Approval of Alternate
Test Procedures for Organic and
Inorganic Analytes in Wastewater and
Drinking Water (EPA–821–B–98–002,
March 1999) and meet the QC
provisions specified therein. In
addition, the Analyst must perform ongoing QC tests, including assessment of
performance of the modified method on
the sample matrix (e.g., analysis of a
matrix spike/matrix spike duplicate pair
for every twenty samples of a discharge
analyzed), and analysis of an ongoing
precision and recovery sample and a
blank with each batch of 20 or fewer
samples.
(C) Calibration must be performed
using the modified method and the
modified method must be tested with
every wastewater matrix to which it will
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be applied (up to nine distinct matrices;
as described in the ATP Protocol, after
validation in nine distinct matrices, the
method may be applied to all
wastewater matrices), in addition to any
and all reagent water tests. If the
performance in the wastewater matrix or
reagent water does not meet the QC
acceptance criteria the method
modification may not be used.
(D) Analysts must test representative
effluents with the modified method, and
demonstrate that the results are
equivalent or superior to results with
the unmodified method.
(ii) Requirements for Documentation.
The modified method must be
documented in a method write-up or an
addendum that describes the
modification(s) to the approved method.
The write-up or addendum must
include a reference number (e.g.,
method number), revision number, and
revision date so that it may be
referenced accurately. In addition, the
organization that uses the modified
method must document the results of
QC tests and keep these records, along
with a copy of the method write-up or
addendum, for review by an auditor.
(3) Restrictions. An analyst may not
modify an approved analytical method
for a method-defined analyte. In
addition, an analyst may not modify an
approved method if the modification
would result in measurement of a
different form or species of an analyte
(e.g., a change to a metals digestion or
total cyanide distillation). An analyst
may also may not modify any sample
preservation and/or holding time
requirements of an approved method.
(c) Analytical Requirements for Multianalyte Methods (Target Analytes). For
the purpose of NPDES reporting, the
discharger or permittee must meet QC
requirements only for the analyte(s)
being measured and reported under the
NPDES permit.
(d) The following modifications to
approved methods are authorized in the
circumstances described below:
(1) Capillary Column. Use of a
capillary (open tubular) GC column
rather than a packed column is allowed
with EPA Methods 601–613, 624, 625,
and 1624B in Appendix A to this part,
provided that all QC tests for the
approved method are performed and all
QC acceptance criteria are met. When
changing from a packed column to a
capillary column, retention times will
change. Analysts are not required to
meet retention time specified in the
approved method when this change is
made. Instead, analysts must generate
new retention time tables with capillary
columns to be kept on file along with
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other startup test and ongoing QC data,
for review by auditors.
(2) Increased sample volume in purge
and trap methodology. Use of increased
sample volumes, up to a maximum of 25
mL, is allowed for an approved method,
provided that the height of the water
column in the purge vessel is at least 5
cm. The analyst should also use one or
more surrogate analytes that are
chemically similar to the analytes of
interest in order to demonstrate that the
increased sample volume does not
adversely affect the analytical results.
PART 141—NATIONAL PRIMARY
DRINKING WATER REGULATIONS
11. The authority citation for part 141
continues to read as follows:
I
Authority: 42 U.S.C. 300f, 300g–1, 300g–2,
300g–3, 300g–4, 300g–5, 300g–6, 300j–4,
300j–9, and 300j–11.
12. Section 141.21 is amended by
adding four sentences to the end of
footnote 1 to the Table in paragraph
(f)(3) to read as follows:
I
§ 141.21
Coliform sampling.
*
*
*
*
*
(f) * * *
(3) * * *
1* * * In addition, the following
online versions may also be used: 9221
A, B, D–99, 9222 A, B, C–97, and 9223
B–97. Standard Methods Online are
available at https://
www.standardmethods.org. The year in
which each method was approved by
the Standard Methods Committee is
designated by the last two digits in the
method number. The methods listed are
the only Online versions that may be
used.
*
*
*
*
*
I 13. Section 141.23 is amended as
follows:
I a. In paragraph (a)(4)(i) by revising the
table entries for ‘‘Cyanide,’’ ‘‘Nitrate,’’
and ‘‘Nitrite’’.
I b. In paragraph (k)(1) by revising the
table.
§ 141.23 Inorganic chemical sampling and
analytical requirements.
*
*
*
(a) * * *
(4) * * *
(i) * * *
*
*
DETECTION LIMITS FOR INORGANIC CONTAMINANTS
Contaminant
MCL (mg/L)
*
Cyanide .....................
0.2
*
Nitrate ........................
*
10 (as N)
Nitrite .........................
1 (as N)
*
*
Methodology
Detection Limit (mg/L)
*
*
*
*
Distillation, Spectrophotometric3 ...........................................................
Distillation, Automated, Spectrophotometric3 .......................................
Distillation, Amenable, Spectrophotometric4 ........................................
Distillation, Selective Electrode3, 4 ........................................................
UV, Distillation, Spectrophotometric9 ....................................................
Micro Distillation, Flow Injection, Spectrophotometric3 ........................
Ligand Exchange with Amperometry4 ..................................................
*
*
*
*
*
Manual Cadmium Reduction ................................................................
Automated Hydrazine Reduction ..........................................................
Automated Cadmium Reduction ...........................................................
Ion Selective Electrode .........................................................................
Ion Chromatography .............................................................................
Capillary Ion Electrophoresis ................................................................
Spectrophotometric ...............................................................................
Automated Cadmium Reduction ...........................................................
Manual Cadmium Reduction ................................................................
Ion Chromatography .............................................................................
Capillary Ion Electrophoresis ................................................................
*
*
*
*
*
0.02
0.005
0.02
0.05
0.0005
0.0006
0.0005
0.01
0.01
0.05
1
0.01
0.076
0.01
0.05
0.01
0.004
0.103
*
*
*
*
*
*
*
3 Screening method for total cyanides.
4 Measures ‘‘free’’ cyanides when distillation, digestion, or ligand exchange is omitted.
*
*
*
*
*
9 Measures total cyanides when UV-digestor is used, and ‘‘free’’ cyanides when UV-digestor is bypassed.
*
*
*
*
*
(k) * * *
(1) * * *
Contaminant
Methodology 13
EPA
ASTM 3
SM 4 (18th, 19th
ed.)
SM 4 (20th ed.)
SM Online 22
1. Alkalinity ..............
Titrimetric ........................
Electrometric titration ......
Inductively Coupled Plasma (ICP)—Mass Spectrometry.
Hydride-Atomic Absorption.
Atomic Absorption; Platform.
Atomic Absorption; Furnace.
Inductively Coupled Plasma 15.
ICP-Mass Spectrometry
....................
....................
200.8 2
D1067–92, 02 B .............
.........................................
2320 B .............
.........................
2320 B .............
.........................
2320 B–97 .......
I–1030–85 5.
....................
D3697–92, 02.
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2. Antimony ..............
3. Arsenic 14 .............
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200.9 2
....................
.........................................
3113 B .............
.........................
3113 B–99 .......
200.7 2 ........
.........................................
3120 B .............
3120 B .............
3120 B–99.
200.8 2
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11242
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Methodology 13
Contaminant
4. Asbestos ..............
5. Barium .................
6. Beryllium ..............
7. Cadmium .............
8. Calcium ................
9. Chromium ............
10. Copper ...............
11. Conductivity .......
12. Cyanide .............
rwilkins on PROD1PC63 with RULES
13. Fluoride ..............
14. Lead ...................
VerDate Aug<31>2005
Atomic Absorption; Platform.
Atomic Absorption; Furnace.
Hydride Atomic Absorption.
Transmission Electron
Microscopy.
Transmission Electron
Microscopy.
Inductively Coupled Plasma.
ICP-Mass Spectrometry
Atomic Absorption; Direct
Atomic Absorption; Furnace.
Inductively Coupled Plasma.
ICP-Mass Spectrometry
Atomic Absorption; Platform.
Atomic Absorption; Furnace.
Inductively Coupled Plasma.
ICP-Mass Spectrometry
Atomic Absorption; Platform.
Atomic Absorption; Furnace.
EDTA titrimetric ..............
Atomic Absorption; Direct
Aspiration.
Inductively Coupled Plasma.
Ion Chromatography .......
Inductively Coupled Plasma.
ICP-Mass Spectrometry
Atomic Absorption; Platform.
Atomic Absorption; Furnace.
Atomic Absorption; Furnace.
Atomic Absorption; Direct
Aspiration.
Inductively Coupled Plasma.
ICP-Mass spectrometry ..
Atomic Absorption; Platform.
Conductance ..................
Manual Distillation followed by
Spectrophotometric,
Amenable.
Spectro-photometric
Manual.
Spectro-photometric
Semi-automated.
Selective Electrode .........
UV, Distillation,
Spectrophotometric.
Micro Distillation, Flow
Injection,
Spectrophotometric.
Ligand Exchange and
Amperometry 21.
Ion Chromatography .......
Manual Distill.; Color.
SPADNS.
Manual Electrode ...........
Automated Electrode ......
Automated Alizarin .........
Capillary Ion Electrophoresis.
Atomic Absorption; Furnace.
ICP–Mass spectrometry
18:34 Mar 09, 2007
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ASTM 3
SM 4 (18th, 19th
ed.)
SM 4 (20th ed.)
....................
D2972–97, 03 C .............
3113 B .............
.........................
3113 B–99.
....................
D2972–97, 03 B .............
3114 B .............
.........................
3114 B–97.
200.7 2 ........
.........................................
3120 B .............
3120 B .............
3120 B–99.
200.8 2
....................
....................
.........................................
.........................................
3111D ..............
3113 B .............
.........................
.........................
3111 D–99.
3113 B–99.
200.7 2 ........
.........................................
3120 B .............
3120 B .............
3120 B–99.
D3645–97, 03 B .............
3113 B .............
.........................
3113 B–99.
....................
.........................................
3113 B .............
.........................
3113 B–99.
....................
....................
D511–93, 03 A ...............
D511–93, 03 B ...............
3500–Ca D ......
3111 B .............
3500–Ca B ......
.........................
3500–Ca B–97.
3111 B–99.
200.7 2 ........
.........................................
3120 B .............
3120 B .............
3120 B–99.
....................
200.7 2 ........
D6919–03.
.........................................
3120 B .............
3120 B .............
3120 B–99.
....................
.........................................
3113 B .............
.........................
3113 B–99.
....................
D1688–95, 02 C .............
3113 B .............
.........................
3113 B–99.
....................
D1688–95, 02 A .............
3111 B .............
.........................
3111 B–99.
200.7 2
........
.........................................
3120 B .............
3120 B .............
3120 B–99.
....................
2510 B .............
2510 B .............
2510 B–97.
....................
D1125–95 (Reapproved
1999) A.
D2036–98 A ...................
4500–CN¥ C ..
4500–CN¥ C.
....................
D2036–98 B ...................
4500–CN¥ G ..
4500–CN¥ G ..
....................
D2036–98 A ...................
4500–CN¥ E ...
4500–CN¥ E ...
....................
.........................................
4500–CN¥ F ...
4500–CN¥ F ...
....................
.........................................
.........................
.........................
4500–CN¥ F–
99.
.........................
....................
.........................................
.........................
.........................
.........................
....................
D6888–04 .......................
.........................
.........................
.........................
300.0 6,
300.1 19
....................
D4327–97, 03 .................
4110 B .............
4110 B .............
4110 B–00.
.........................................
4500–F¥ B, D
4500–F¥ B, D
....................
....................
....................
....................
D1179–93, 99 B .............
.........................................
.........................................
.........................................
4500–F¥ C .....
.........................
4500–F¥ E ......
.........................
4500–F¥ C .....
.........................
4500–F¥ E ......
.........................
4500–F¥ B, D–
97.
4500–F¥ C–97.
.........................
4500–F¥ E–97
.........................
....................
D3559–96, 03 D .............
3113 B .............
.........................
3113 B–99.
EPA
SM Online 22
Other
200.9 2
100.1 9
100.2 10
200.8 2
200.9 2
....................
200.7 2
200.8 2
200.9 2
200.8 2
200.9 2
200.8 2
200.9 2
4500–CN¥ G–
99.
4500–CN¥ E–
99.
I–3300–85 5
335.4 6
200.8 2
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Kelada–01 17
QuikChem 10–
204–00–1–
X 18
OIA–1677,
DW 20
380–75WE 11
129–71W 11
D6508, Rev.
2 23
11243
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
Methodology 13
Contaminant
15. Magnesium ........
16. Mercury ..............
17. Nickel .................
18. Nitrate ................
Atomic Absorption; Platform.
Differential Pulse Anodic
Stripping Voltametry.
Atomic Absorption ..........
ICP ..................................
Complexation Titrimetric
Methods.
Ion Chromatography .......
Manual, Cold Vapor .......
Automated, Cold Vapor ..
ICP–Mass Spectrometry
Inductively Coupled Plasma.
ICP–Mass Spectrometry
Atomic Absorption; Platform.
Atomic Absorption; Direct
Atomic Absorption; Furnace.
Ion Chromatography .......
Automated Cadmium Reduction.
Ion Selective Electrode ..
19. Nitrite .................
Manual Cadmium Reduction.
Capillary Ion Electrophoresis.
Ion Chromatography .......
ASTM 3
SM 4 (18th, 19th
ed.)
SM 4 (20th ed.)
SM Online 22
Other
....................
.........................................
.........................
.........................
.........................
Method 1001 16
....................
200.7 2 ........
....................
D511–93, 03 B ...............
.........................................
D511–93, 03 A ...............
3111 B .............
3120 B .............
3500–Mg E ......
.........................
3120 B .............
3500–Mg B ......
3111 B–99.
3120 B–99.
3500–Mg B–97.
....................
245.1 2 ........
245.2 1
200.8 2
200.7 2 ........
D6919–03.
D3223–97, 02 .................
3112 B .............
.........................
3112 B–99.
.........................................
3120 B .............
3120 B .............
3120 B–99.
....................
....................
.........................................
.........................................
3111 B .............
3113 B .............
.........................
.........................
3111 B–99.
3113 B–99.
300.0 6
300.1 19
353.2 6 ........
D4327–97, 03 .................
4110 B .............
4110 B .............
4110 B–00 .......
D3867–90 A ...................
4500–NO3¥ F
4500–NO3¥ F
....................
.........................................
4500–NO3¥ D
4500–NO3¥ D
....................
D3867–90 B ...................
4500–NO3¥ E
4500–NO3¥ E
....................
.........................................
.........................
.........................
4500–NO3¥ F–
00.
4500–NO3¥ D–
00.
4500–NO3¥ E–
00.
.........................
300.0 6
D4327–97, 03 .................
4110 B .............
4110 B .............
4110 B–00 .......
EPA
200.9 2
200.8 2
200.9 2
B–1011 8
601 7
D6508, Rev.
2 23
B–1011 8
300.1 19
353.2 6 ........
D3867–90 A ...................
4500–NO3
....................
D3867–90 B ...................
4500–NO3¥ E
4500–NO3¥ E
....................
.........................................
4500–NO2¥ B
4500–NO2¥ B
....................
.........................................
.........................
.........................
365.1 6
........
.........................................
4500–P F ........
4500–P F.
....................
D515–88 A .....................
4500–P E ........
4500–P E.
....................
.........................................
.........................
.........................
.........................
I–1601–85 5
....................
.........................................
.........................
.........................
.........................
I–2601–90 5
....................
300.0 6 ........
300.1 19 ......
....................
.........................................
D4327–97, 03 .................
.........................
4110 B .............
.........................
4110 B .............
.........................
4110 B–00.
I–2598–85 5
.........................................
.........................
.........................
.........................
D6508, Rev.
2 23
D1293–95, 99 .................
4500–H∂
4500–H∂
4500–H∂
D3859–98, 03 A .............
3114 B .............
.........................
3114 B–97.
....................
D3859–98, 03 B .............
3113 B .............
.........................
3113 B–99.
....................
.........................................
.........................
.........................
.........................
I–1700–85 5
....................
.........................................
.........................
.........................
.........................
I–2700–85 5
....................
....................
D859–94, 00.
.........................................
4500–Si D .......
4500–SiO2 C ...
Heteropoly blue ..............
....................
.........................................
4500–Si E .......
4500–SiO2 D ...
Automated for Molybdate-reactive Silica.
Inductively Coupled Plasma.
Inductively Coupled Plasma.
Atomic Absorption; Direct
Aspiration.
Ion Chromatography .......
Thermometric .................
ICP–Mass Spectrometry
....................
.........................................
4500–Si F ........
4500–SiO2 E ...
200.7 2 ........
.........................................
3120 B .............
3120 B .............
4500–SiO2 C–
97.
4500–SiO2 D–
97.
4500–SiO2 E–
97.
3120 B–99.
....................
.........................................
3111 B .............
.........................
3111 B–99.
....................
....................
200.8 2
D6919–03.
.........................................
2550 ................
2550 ................
2550–00.
Automated Cadmium Reduction.
Manual Cadmium Reduction.
Spectrophotometric ........
Capillary Ion Electrophoresis.
Colorimetric, Automated,
Ascorbic Acid.
Colorimetric, ascorbic
acid, single reagent.
Colorimetric
Phosphomolybdate;
Automated-segmented flow;
Automated Discrete
Ion Chromatography .......
20. Ortho-phosphate 12.
21. pH ......................
22. Selenium ............
rwilkins on PROD1PC63 with RULES
23. Silica ..................
24. Sodium ..............
25. Temperature ......
26. Thallium .............
VerDate Aug<31>2005
Capillary Ion Electrophoresis.
Electrometric ...................
Hydride-Atomic Absorption.
ICP–Mass Spectrometry
Atomic Absorption; Platform.
Atomic Absorption; Furnace.
Colorimetric, Molybdate
Blue.
Automated-segmented Flow.
Colorimetric ....................
Molybdosilicate ...............
18:34 Mar 09, 2007
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150.1,
150.2 1
....................
¥
F
B .....
¥
4500–NO3
F
B .....
4500–NO3¥ F–
00.
4500–NO3¥ E–
00.
4500–NO2¥ B–
00.
.........................
D6508, Rev.
2 23
B–00.
200.8 2
200.9 2
200.7 2
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11244
Contaminant
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
Methodology 13
SM 4 (18th, 19th
ed.)
ASTM 3
EPA
SM 4 (20th ed.)
SM Online 22
Other
200.9 2.
Atomic Absorption; Platform.
The procedures shall be done in accordance with the documents listed below. The incorporation by reference of the following documents listed in footnotes 1–11, 16–20, and 22–23 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 below. Information regarding obtaining these documents can be obtained from the Safe Drinking Water Hotline at 800–426–4791. Documents may be inspected at EPA’s Drinking Water Docket, EPA West,
1301 Constitution Avenue, NW., Room 3334, Washington, DC 20460 (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.
1 ‘‘Methods for Chemical Analysis of Water and Wastes,’’ EPA/600/4–79/020, March 1983. Available at NTIS, PB84–128677.
2 ‘‘Methods for the Determination of Metals in Environmental Samples—Supplement I,’’ EPA/600/R–94/111, May 1994. Available at NTIS, PB95–125472.
3 Annual Book of ASTM Standards, 1994, 1996, 1999, or 2003, Vols. 11.01 and 11.02, ASTM International; any year containing the cited version of the method may be used. The previous
versions of D1688–95A, D1688–95C (copper), D3559–95D (lead), D1293–95 (pH), D1125–91A (conductivity) and D859–94 (silica) are also approved. These previous versions D1688–90A, C;
D3559–90D, D1293–84, D1125–91A and D859–88, respectively are located in the Annual Book of ASTM Standards, 1994, Vol. 11.01. Copies may be obtained from ASTM International, 100
Barr Harbor Drive, West Conshohocken, PA 19428.
4 Standard Methods for the Examination of Water and Wastewater, 18th edition (1992), 19th edition (1995), or 20th edition (1998). American Public Health Association, 1015 Fifteenth
Street, NW., Washington, DC 20005. The cited methods published in any of these three editions may be used, except that the versions of 3111 B, 3111 D, 3113 B and 3114 B in the 20th
edition may not be used.
5 Method I–2601–90, Methods for Analysis by the U.S. Geological Survey National Water Quality Laboratory—Determination of Inorganic and Organic Constituents in Water and Fluvial
Sediment, Open File Report 93–125, 1993; For Methods I–1030–85; I–1601–85; I–1700–85; I–2598–85; I–2700–85; and I–3300–85 See Techniques of Water Resources Investigation of the
U.S. Geological Survey, Book 5, Chapter A–1, 3rd edition., 1989; Available from Information Services, U.S. Geological Survey, Federal Center, Box 25286, Denver, CO 80225–0425.
6 ‘‘Methods for the Determination of Inorganic Substances in Environmental Samples,’’ EPA/600/R–93/100, August 1993. Available at NTIS, PB94–120821.
7 The procedure shall be done in accordance with the Technical Bulletin 601 ’’ Standard Method of Test for Nitrate in Drinking Water,’’ July 1994, PN 221890–001, Analytical Technology,
Inc. Copies may be obtained from ATI Orion, 529 Main Street, Boston, MA 02129.
8 Method B–1011, ‘‘Waters Test Method for Determination of Nitrite/Nitrate in Water Using Single Column Ion Chromatography,’’ August 1987. Copies may be obtained from Waters Corporation, Technical Services Division, 34 Maple Street, Milford, MA 01757, Telephone: 508/482–2131, Fax: 508/482–3625.
9 Method 100.1, ‘‘Analytical Method For Determination of Asbestos Fibers in Water,’’ EPA/600/4–83/043, EPA, September 1983. Available at NTIS, PB83–260471.
10 Method 100.2, ‘‘Determination of Asbestos Structure Over 10-µm In Length In Drinking Water,’’ EPA/600/R–94/134, June 1994. Available at NTIS, PB94–201902.
11 Industrial Method No. 129–71W, ‘‘Fluoride in Water and Wastewater,’’ December 1972, and Method No. 380–75WE, ‘‘Fluoride in Water and Wastewater,’’ February 1976, Technicon Industrial Systems. Copies may be obtained from Bran & Luebbe, 1025 Busch Parkway, Buffalo Grove, IL 60089.
12 Unfiltered, no digestion or hydrolysis.
13 Because MDLs reported in EPA Methods 200.7 and 200.9 were determined using a 2x preconcentration step during sample digestion, MDLs determined when samples are analyzed by
direct analysis (i.e., no sample digestion) will be higher. For direct analysis of cadmium and arsenic by Method 200.7, and arsenic by Method 3120 B, sample preconcentration using pneumatic nebulization may be required to achieve lower detection limits. Preconcentration may also be required for direct analysis of antimony, lead, and thallium by Method 200.9; antimony and
lead by Method 3113 B; and lead by Method D3559–90D, unless multiple in-furnace depositions are made.
14 If ultrasonic nebulization is used in the determination of arsenic by Methods 200.7, 200.8, or SM 3120 B, the arsenic must be in the pentavalent state to provide uniform signal response.
For Methods 200.7 and 3120 B, both samples and standards must be diluted in the same mixed acid matrix concentration of nitric and hydrochloric acid with the addition of 100 µL of 30%
hydrogen peroxide per 100 mL of solution. For direct analysis of arsenic with Method 200.8 using ultrasonic nebulization, samples and standards must contain 1 mg/L of sodium hypochlorite.
15 Starting January 23, 2006, analytical methods using the ICP–AES technology may not be used because the detection limits for these methods are 0.008 mg/L or higher. This restriction
means that the two ICP–AES methods (EPA Method 200.7 and SM 3120 B) approved for use for the MCL of 0.05 mg/L may not be used for compliance determinations for the revised MCL
of 0.010 mg/L. However, prior to January 23, 2006, systems may have compliance samples analyzed with these less sensitive methods.
16 The description for Method Number 1001 for lead is available from Palintest, LTD, 21 Kenton Lands Road, P.O. Box 18395, Erlanger, KY 41018. Or from the Hach Company, P.O. Box
389, Loveland, CO 80539.
17 The description for the Kelada-01 Method, ‘‘Kelada Automated Test Methods for Total Cyanide, Acid Dissociable Cyanide, And Thiocyanate,’’ Revision 1.2, August 2001, EPA # 821–B–
01–009 for cyanide is available from the National Technical Information Service (NTIS), PB 2001–108275, 5285 Port Royal Road, Springfield, VA 22161. The toll free telephone number is
800–553–6847. Note: A 450–W UV lamp may be used in this method instead of the 550–W lamp specified if it provides performance within the quality control (QC) acceptance criteria of the
method in a given instrument. Similarly, modified flow cell configurations and flow conditions may be used in the method, provided that the QC acceptance criteria are met.
18 The description for the QuikChem Method 10–204–00–1–X, ‘‘Digestion and distillation of total cyanide in drinking and wastewaters using MICRO DIST and determination of cyanide by
flow injection analysis,’’ Revision 2.1, November 30, 2000, for cyanide is available from Lachat Instruments, 6645 W. Mill Rd., Milwaukee, WI 53218. Telephone: 414–358–4200.
19 ‘‘Methods for the Determination of Organic and Inorganic Compounds in Drinking Water,’’ Vol. 1, EPA 815–R–00–014, August 2000. Available at NTIS, PB2000–106981.
20 Method OIA–1677, DW ‘‘Available Cyanide by Flow Injection, Ligand Exchange, and Amperometry,’’ January 2004. EPA–821–R–04–001, Available from ALPKEM, A Division of OI Analytical, P.O. Box 9010, College Station, TX 77842–9010.
21 Sulfide levels below those detected using lead acetate paper may produce positive method interferences. Test samples using a more sensitive sulfide method to determine if a sulfide interference is present, and treat samples accordingly.
22 Standard Methods Online are available at https://www.standardmethods.org. The year in which each method was approved by the Standard Methods Committee is designated by the last
two digits in the method number. The methods listed are the only online versions that may be used.
23 Method D6508, Rev. 2, ‘‘Test Method for Determination of Dissolved Inorganic Anions in Aqueous Matrices Using Capillary Ion Electrophoresis and Chromate Electrolyte,’’ available from
Waters Corp, 34 Maple St, Milford, MA, 01757, Telephone: 508/482–2131, Fax: 508/482–3625.
*
*
*
*
*
14. Section 141.24 is amended as
follows:
I a. By revising the introductory text of
paragraph (e)(1).
I b. By revising entries 23, 24, 26, 30,
49, and 50 in the table to paragraph
(e)(1).
I c. By adding a new footnote 5 to the
table to paragraph (e)(1).
I
§ 141.24 Organic chemicals, sampling and
analytical requirements.
rwilkins on PROD1PC63 with RULES
*
*
*
*
*
(e) * * *
(1) The following documents are
incorporated by reference. This
incorporation by reference was
approved by the Director of the Federal
Register in accordance with 5 U.S.C.
552(a) and 1 CFR Part 51. Copies may
be inspected at EPA’s Drinking Water
Docket, 1301 Constitution Avenue, NW.,
EPA West, Room 3334, Washington, DC
20460 (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/
VerDate Aug<31>2005
18:34 Mar 09, 2007
Jkt 211001
federal_register/
code_of_federal_regulations/
ibr_locations.html. Method 508A and
515.1 are in Methods for the
Determination of Organic Compounds
in Drinking Water, EPA/600/4–88–039,
December 1988, Revised, July 1991.
Methods 547, 550 and 550.1 are in
Methods for the Determination of
Organic Compounds in Drinking
Water—Supplement I, EPA/600–4–90–
020, July 1990. Methods 548.1, 549.1,
552.1 and 555 are in Methods for the
Determination of Organic Compounds
in Drinking Water—Supplement II,
EPA/600/R–92–129, August 1992.
Methods 502.2, 504.1, 505, 506, 507,
508, 508.1, 515.2, 524.2 525.2, 531.1,
551.1 and 552.2 are in Methods for the
Determination of Organic Compounds
in Drinking Water––Supplement III,
EPA/600/R–95–131, August 1995.
Method 1613 is titled ‘‘Tetra–through
Octa–Chlorinated Dioxins and Furans
by Isotope–Dilution HRGC/HRMS,’’
EPA/821–B–94–005, October 1994.
These documents are available from the
National Technical Information Service,
NTIS PB91–231480, PB91–146027,
PO 00000
Frm 00046
Fmt 4701
Sfmt 4700
PB92–207703, PB95–261616 and PB95–
104774, U.S. Department of Commerce,
5285 Port Royal Road, Springfield,
Virginia 22161. The toll free number is:
800–553–6847. Method 6651 shall be
followed in accordance with Standard
Methods for the Examination of Water
and Wastewater, 18th edition (1992),
19th edition (1995), or 20th edition
(1998), American Public Health
Association (APHA); any of these three
editions may be used. Method 6610
shall be followed in accordance with
Standard Methods for the Examination
of Water and Wastewater, (18th Edition
Supplement) (1994), or with the 19th
edition (1995) or 20th edition (1998) of
Standard Methods for the Examination
of Water and Wastewater; any of these
publications may be used. The APHA
documents are available from APHA,
1015 Fifteenth Street NW., Washington,
DC 20005. Other required analytical test
procedures germane to the conduct of
these analyses are contained in
Technical Notes on Drinking Water
Methods, EPA/600/R–94–173, October
1994, NTIS PB95–104766. EPA Methods
515.3 and 549.2 are available from U.S.
E:\FR\FM\12MRR2.SGM
12MRR2
11245
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
Environmental Protection Agency,
National Exposure Research Laboratory
(NERL)–Cincinnati, 26 West Martin
Luther King Drive, Cincinnati, OH
45268. ASTM Method D 5317–93, 98
(Reapproved 2003) is available in the
Annual Book of ASTM Standards,
(1999), Vol. 11.02, ASTM International,
100 Barr Harbor Drive, West
Conshohocken, PA 19428, any edition
containing the cited version of the
method may be used. EPA Method
515.4, ‘‘Determination of Chlorinated
Acids in Drinking Water by LiquidLiquid Microextraction, Derivatization
and Fast Gas Chromatography with
Electron Capture Detection,’’ Revision
1.0, April 2000, EPA/815/B–00/001 and
EPA Method 552.3, ‘‘Determination of
Haloacetic Acids and Dalapon in
Drinking Water by Liquid-Liquid
Microextraction, Derivatization, and Gas
Chromatography with Electron Capture
Detection,’’ Revision 1.0, July 2003, EPA
815–B–03–002, can be accessed and
downloaded directly online at https://
www.epa.gov/safewater/methods/
sourcalt.html. Syngenta Method AG–
625, ‘‘Atrazine in Drinking Water by
Immunoassay,’’ February 2001, is
Contaminant
Standard
Methods
EPA Method1
*
*
*
23. 2,4–D 4 (as acids, salts, and esters) ............................................
24. 2,4,5–TP 4 (Silvex) ........................................................................
*
515.2, 555,
515.1, 515.3,
515.4.
515.2, 555,
515.1, 515.3,
515.4.
*
*
*
26. Atrazine 2 .......................................................................................
*
507, 525.2,
508.1, 505,
551.1.
*
*
*
30. Dalapon ........................................................................................
*
515.2, 525.2,
555, 515.1,
515.3, 515.4.
515.2, 555,
515.1, 515.3,
515.4.
50. Picloram 4 ......................................................................................
*
*
*
ASTM
*
....................
*
....................
*
*
............................
*
Syngenta 5 AG–625
*
*
*
*
....................
*
D5317–93, 98
(Reapproved
2003).
D5317–93, 98
(Reapproved
2003).
....................
*
Other
*
D5317–93, 98
(Reapproved
2003).
D5317–93, 98
(Reapproved
2003).
....................
*
552.1 515.1,
552.2, 515.3,
515.4, 552.3.
*
*
*
49. Pentachlorophenol ........................................................................
available from Syngenta Crop
Protection, Inc., 410 Swing Road, P.O.
Box 18300, Greensboro, NC 27419.
Telephone: 336–632–6000. Method
531.2 ‘‘Measurement of Nmethylcarbamoyloximes and Nmethylcarbamates in Water by Direct
Aqueous Injection HPLC with
Postcolumn Derivatization,’’ Revision
1.0, September 2001, EPA 815–B–01–
002, can be accessed and downloaded
directly online at https://www.epa.gov/
safewater/methods/sourcalt.html.
*
*
*
*
1 For
previously approved EPA methods which remain available for compliance monitoring until June 1, 2001, see paragraph (e)(2) of this section.
2 Substitution of the detector specified in Method 505, 507, 508, or 508.1 for the purpose of achieving lower detection limits is allowed as follows: Either an electron capture or nitrogen phosphorus detector may be used provided all regulatory requirements and quality control criteria are
met.
*
*
*
*
*
4 Accurate determination of the chlorinated esters requires hydrolysis of the sample as described in EPA Methods 515.1, 515.2, 515.3, 515.4,
and 555 and ASTM Method D 5317–93, 98 (Reapproved 2003).
5 This method may not be used for the analysis of atrazine in any system where chlorine dioxide is used for drinking water treatment. In samples from all other systems, any result for atrazine generated by Method AG–625 that is greater than one-half the maximum contaminant level
(MCL) (in other words, greater than 0.0015mg/L or 1.5 µg/L) must be confirmed using another approved method for this contaminant and should
use additional volume of the original sample collected for compliance monitoring. In instances where a result from Method AG–625 triggers such
confirmatory testing, the confirmatory result is to be used to determine compliance.
*
*
*
*
*
§ 141.25 Analytical methods for
radioactivity.
15. Section 141.25 is amended by
revising the table in paragraph (a) to
read as follows:
I
(a) * * *
Reference (Method of Page Number)
Contaminant
Methodology
rwilkins on PROD1PC63 with RULES
EPA 1
EPA 2
EPA 3
EPA 4
SM 5
ASTM 6
USGS 7
302, 7110 B,
7110 B–00.
7110 C, 7110
C–00.
................
R–1120–76.
Naturally Occurring:
Gross alpha 11 and beta .....
Evaporation ............
900.0
p. 1 ...
00–01
p. 1 ........
Gross alpha 11 .....................
Coprecipitation .......
................
..........
00–02
...............
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Other
11246
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Reference (Method of Page Number)
Contaminant
Methodology
EPA 1
Radium 226 ........................
EPA 2
EPA 3
EPA 4
SM 5
ASTM 6
305, 7500–Ra
C, 7500–
Ra C–01.
304, 7500–Ra
B, 7500–Ra
B–01.
7500–Ra D,
7500–Ra
D–01.
7500–U B,
7500–U B–
00.
7500–U C
(17th Ed.).
D3454–97
R–1141–76
Ra-04 .....
NY 9,
D2460–97
R–1140–76
................
GA 14
................
R–1142–76
................
NY 9,
NJ 10,
GA 14
D2907–97
R–1180–76,
R–1181–
76.
U–04.
3125 .............
7500–U C
(18th, 19th,
or 20th
Ed.), 7500–
U C–00.
......................
D5673–03.
D3972–
R–1182–76
97, 02.
Radon emanation ...
903.1
p. 16
Ra–04
p. 19 ......
Radiochemical ........
903.0
p. 13
Ra-03
...............
Radium 228 ........................
Radiochemical ........
904.0
p. 24
Ra-05
p. 19 ......
Uranium 12 ...........................
Radiochemical ........
908.0
..........
............
...............
Fluorometric ...........
908.1
..........
............
...............
ICP–MS ..................
Alpha Spectrometry
200.8 13
................
..........
..........
............
00–07
...............
p. 33 ......
Laser
Phosphorimetry.
................
..........
............
...............
Man-Made:
Radioactive Cesium ............
Radiochemical ........
901.0
p. 4 ...
............
...............
901.1
..........
............
p. 92 ......
Radioactive Iodine ..............
Gamma Ray Spectrometry.
Radiochemical ........
902.0
p. 6 ...
............
...............
p. 9 ...
............
...............
Gamma Ray Spectrometry.
Radiochemical ........
901.1
..........
............
p. 92 ......
905.0
p. 29
Sr–04
p. 65 ......
Tritium .................................
Liquid Scintillation ..
906.0
p. 34
H–02 ..
p. 87 ......
Gamma Emitters .................
Gamma Ray Spectrometry.
901.1
..........
............
p. 92 ......
902.0
..........
............
...............
901.0
..........
............
...............
rwilkins on PROD1PC63 with RULES
Radioactive Strontium 89,
90.
7500–Cs B,
7500–Cs
B–00.
7120, 7120–
97.
7500–I B,
7500–I B–
00.
7500–I C,
7500–I C–
00.
7500–I D,
7500–I D–
00.
7120, 7120–
97.
303, 7500–Sr
B, 7500–Sr
B–01.
306, 7500–
3 H B,
7500–3 H
B–00.
7120, 7120–
97.
7500–Cs B,
7500–Cs
B–00.
7500–I B,
7500–I B–
00.
USGS 7
DOE 8
Other
U–02.
D5174–
97, 02.
D2459–72
R–1111–76.
D3649–
91, 98a.
R–1110–76
4.5.2.3.
....................
4.5.2.3.
R–1160–76
Sr–01,
Sr–02.
D3649–
91, 98a.
D4785–
93, 00a.
................
D4107–
91, 98
(Reapproved
2002).
D3649–
91, 98a.
D4785–
93, 00a.
R–1171–76.
R–1110–76
Ga–01–R.
The procedures shall be done in accordance with the documents listed below. The incorporation by reference of documents 1 through 10 and 13 through 14 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 below. Information regarding obtaining
these documents can be obtained from the Safe Drinking Water Hotline at 800–426–4791. Documents may be inspected at EPA’s Drinking Water Docket, EPA West, 1301 Constitution Avenue, NW., Room 3334 , Washington, DC 20460 (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.
1 ‘‘Prescribed Procedures for the Measurement of Radioactivity in Drinking Water,’’ EPA 600/4–80–032, August 1980. Available at the U.S. Department of Commerce, National Technical Information Service (NTIS), 5285 Port Royal Road, Springfield, VA 22161 (Telephone 800–553–6847), PB 80–224744.
2 ‘‘Interim Radiochemical Methodology for Drinking Water,’’ EPA 600/4–75–008 (revised), March 1976. Available NTIS, ibid.
3 ‘‘Radiochemistry Procedures Manual,’’ EPA 520/5–84–006, December 1987. Available NTIS, ibid.
4 ‘‘Radiochemical Analytical Procedures for Analysis of Environmental Samples,’’ March 1979. Available at NTIS, ibid. EMSL LV 053917.
5 ‘‘Standard Methods for the Examination of Water and Wastewater,’’ 13th, 17th, 18th, 19th or 20th edition, 1971, 1989, 1992, 1995, 1998. Available at American Public Health Association,
1015 Fifteenth Street, NW., Washington, DC 20005. Methods 302, 303, 304, 305 and 306 are only in the 13th edition. Methods 7110B, 7500–Ra B, 7500–Ra C, 7500–Ra D, 7500–U B,
7500–Cs B, 7500–I B, 7500–I C, 7500–I D, 7500–Sr B, and 7500–3H B are in the 17th, 18th, 19th and 20th editions. Method 7110 C is in the 18th, 19th and 20th editions. Method 7500–U
C Fluorometric Uranium is only in the 17th Edition, and 7500–U C Alpha spectrometry is only in the 18th, 19th and 20th editions. Method 7120 is only in the 19th and 20th editions. Method
3125 is only in the 20th edition. Methods 7110 B–00, 7110 C–00, 7500–Ra B–01, 7500–Ra C–01, 7500–Ra D–01, 7500–U B–00, 7500–U C–00, 7500–I B–00, 7500–I C–00, 7500–I D–00,
7120–97, 7500–Sr B–01, and 7500–3H B–00 are available online at https://www.standardmethods.org. The year in which each method was approved by the Standard Methods Committee is
designated by the last two digits in the method number. The methods listed are the only online versions that may be used.
6 Annual Book of ASTM Standards, Vol. 11.01 and 11.02, 2002; ASTM International; any year containing the cited version of the method may be used. Copies of these two volumes and
the 2003 version of D 5673–03 may be obtained from ASTM International, 100 Barr Harbor Drive, P.O. Box C700, West Conshohocken, PA 19428–2959.
7 ‘‘Methods for Determination of Radioactive Substances in Water and Fluvial Sediments,’’ Chapter A5 in Book 5 of Techniques of Water-Resources Investigations of the United States Geological Survey, 1977. Available at U.S. Geological Survey (USGS) Information Services, Box 25286, Federal Center, Denver, CO 80225–0425.
8 ‘‘EML Procedures Manual,’’ 28th (1997) or 27th (1990) Editions, Volumes 1 and 2; either edition may be used. In the 27th Edition Method Ra-04 is listed as Ra-05 and Method Ga-01–R
is listed as Sect. 4.5.2.3. Available at the Environmental Measurements Laboratory, U.S. Department of Energy (DOE), 376 Hudson Street, New York, NY 10014–3621.
9 ‘‘Determination of Ra–226 and Ra–228 (Ra–02),’’ January 1980, Revised June 1982. Available at Radiological Sciences Institute for Laboratories and Research, New York State Department of Health, Empire State Plaza, Albany, NY 12201.
10 ‘‘Determination of Radium 228 in Drinking Water,’’ August 1980. Available at State of New Jersey, Department of Environmental Protection, Division of Environmental Quality, Bureau of
Radiation and Inorganic Analytical Services, 9 Ewing Street, Trenton, NJ 08625.
11 Natural uranium and thorium-230 are approved as gross alpha calibration standards for gross alpha with co-precipitation and evaporation methods; americium-241 is approved with coprecipitation methods.
12 If uranium (U) is determined by mass, a 0.67 pCi/µg of uranium conversion factor must be used. This conversion factor is based on the 1:1 activity ratio of U–234 and U–238 that is
characteristic of naturally occurring uranium.
13 ‘‘Determination of Trace Elements in Waters and Wastes by Inductively Coupled Plasma-Mass Spectrometry,’’ Revision 5.4, which is published in ‘‘Methods for the Determination of Metals in Environmental Samples—Supplement I,’’ ’ EPA 600–R–94–111, May 1994. Available at NTIS, PB 95–125472.
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14 ‘‘The Determination of Radium-226 and Radium-228 in Drinking Water by Gamma-ray Spectrometry Using HPGE or Ge(Li) Detectors,’’ Revision 1.2, December 2004. Available from the
Environmental Resources Center, Georgia Institute of Technology, 620 Cherry Street, Atlanta, GA 30332–0335, USA, Telephone: 404–894–3776. This method may be used to analyze for radium-226 and radium-228 in samples collected after January 1, 2005 to satisfy the radium-226 and radium-228 monitoring requirements specified at 40 CFR 141.26.
*
*
*
*
*
16. Section 141.74 is amended as
follows:
I a. By revising the entry for turbidity
in the table in paragraph (a)(1).
b. By revising footnotes 1, 8, 10, 11,
and 12 to the table in paragraph (a)(1).
I c. By adding footnote 13 to the table
in paragraph (a)(1).
I d. By revising paragraph (a)(2).
I
I
§ 141.74 Analytical and monitoring
requirements.
(a) * * *
(1) * * *
Citation 1
Organism
Methodology
*
Turbidity 13 .....................
*
*
*
*
*
Nephelometric Method ........................................................................................................................
Nephelometric Method ........................................................................................................................
Great Lakes Instruments .....................................................................................................................
Hach FilterTrak ....................................................................................................................................
*
2130 B
180.1 9
Method 2 10
10133 12
*
*
*
*
*
where noted, all methods refer to Standard Methods for the Examination of Water and Wastewater, 18th edition (1992), 19th edition
(1995), or 20th edition (1998), American Public Health Association, 1015 Fifteenth Street, NW., Washington, DC 20005. The cited methods published in any of these three editions may be used. In addition, the following online versions may also be used: 2130 B–01, 9215 B–00, 9221 A,
B, C, E–99, 9222 A, B, C, D–97, and 9223 B–97. Standard Methods Online are available at https://www.standardmethods.org. The year in which
each method was approved by the Standard Methods Committee is designated by the last two digits in the method number. The methods listed
are the only Online versions that may be used.
*
*
*
*
*
8 A–1 broth may be held up to 7 days in a tightly closed screw cap tube at 4 °C.
9 ‘‘Methods for the Determination of Inorganic Substances in Environmental Samples,’’ EPA/600/R–93/100, August 1993. Available at NTIS,
PB94–121811.
10 GLI Method 2, ‘‘Turbidity,’’ November 2, 1992, Great Lakes Instruments, Inc., 8855 North 55th Street, Milwaukee, WI 53223.
11 A description of the SimPlate method, ‘‘IDEXX SimPlate TM HPC Test Method for Heterotrophs in Water,’’ November 2000, can be obtained
from IDEXX Laboratories, Inc., 1 IDEXX Drive, Westbrook, ME 04092, telephone (800) 321–0207.
12 A description of the Hach FilterTrak Method 10133, ‘‘Determination of Turbidity by Laser Nephelometry,’’ January 2000, Revision 2.0, can be
obtained from; Hach Co., P.O. Box 389, Loveland, CO 80539–0389, telephone: 800–227–4224.
13 Styrene divinyl benzene beads (e.g. AMCO-AEPA–1 or equivalent) and stabilized formazin (e.g. Hach StablCal TM or equivalent) are acceptable substitutes for formazin.
1 Except
(2) Public water systems must
measure residual disinfectant
concentrations with one of the
analytical methods in the following
table. If approved by the State, residual
disinfectant concentrations for free
chlorine and combined chlorine also
may be measured by using DPD
colorimetric test kits. In addition States
may approve the use of the ITS free
chlorine test strip for the determination
of free chlorine. Use of the test strips is
described in Method D99–003, ‘‘Free
Chlorine Species (HOCl- and OCl-) by
Test Strip,’’ Revision 3.0, November 21,
2003, available from Industrial Test
Systems, Inc., 1875 Langston St., Rock
Hill, SC 29730. Free and total chlorine
residuals may be measured
continuously by adapting a specified
SM 1
Residual
Methodology
Free Chlorine .............
Amperometric Titration ...................................
DPD Ferrous Titrimetric .................................
DPD Colorimetric ...........................................
Syringaldazine (FACTS) ................................
Amperometric Titration ...................................
Amperometric Titration (low level measurement).
DPD Ferrous Titrimetric .................................
DPD Colorimetric ...........................................
Iodometric Electrode ......................................
Amperometric Titration ...................................
DPD Method ...................................................
Amperometric Titration ...................................
Spectrophotometric ........................................
Indigo Method ................................................
Total Chlorine .............
Chlorine Dioxide .........
rwilkins on PROD1PC63 with RULES
Ozone .........................
4500–Cl
4500–Cl
4500–Cl
4500–Cl
4500–Cl
4500–Cl
D
F
G
H
D
E
..................
..................
..................
..................
..................
..................
4500–Cl F ..................
4500–Cl G ..................
4500–Cl I ...................
4500–ClO2 C .............
4500–ClO2 D.
4500–ClO2 E ..............
....................................
4500–O3 B .................
chlorine residual method for use with a
continuous monitoring instrument
provided the chemistry, accuracy, and
precision remain the same. Instruments
used for continuous monitoring must be
calibrated with a grab sample
measurement at least every five days, or
with a protocol approved by the State.
SM Online 2
4500–Cl
4500–Cl
4500–Cl
4500–Cl
4500–Cl
4500–Cl
D–00 ............
F–00.
G–00.
H–00.
D–00 ............
E–00.
Other
D1253–03 3
D1253–03 3
4500–Cl F–00.
4500–Cl G–00.
4500–Cl I–00.
4500–ClO2 C–00.
4500–ClO2 E–00.
....................................
4500–O3 B–97.
327.0, Revision 1.1 4
1 All the listed methods are contained in the 18th, 19th, and 20th editions of Standard Methods for the Examination of Water and Wastewater,
1992, 1995, and 1998; the cited methods published in any of these three editions may be used.
2 Standard Methods Online are available at https://www.standardmethods.org. The year in which each method was approved by the Standard
Methods Committee is designated by the last two digits in the method number. The methods listed are the only Online versions that may be
used.
3 Annual Book of ASTM Standards, Vol. 11.01, 2004 ; ASTM International; any year containing the cited version of the method may be used.
Copies of this method may be obtained from ASTM International, 100 Barr Harbor Drive, P.O. Box C700 West Conshohocken, PA 19428–2959.
4 EPA Method 327.0, Revision 1.1, ‘‘Determination of Chlorine Dioxide and Chlorite Ion in Drinking Water Using Lissamine Green B and Horseradish Peroxidase with Detection by Visible Spectrophotometry,’’ USEPA, May 2005, EPA 815–R–05–008. Available online at https://
www.epa.gov/safewater/methods/sourcalt.html.
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*
*
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules and Regulations
*
*
Authority: 42 U.S.C. 300f et seq.
*
PART 143—NATIONAL SECONDARY
DRINKING WATER REGULATIONS
17. The authority citation for part 143
continues to read as follows:
I
Contaminant
1. Aluminum ......................
18. Section § 143.4 is amended by
revising the table in paragraph (b) to
read as follows:
I
ASTM 3
EPA
200.7 2
SM 4 18th and 19th ed.
B
B
D
B
Monitoring.
*
*
(b) * * *
SM 4 20th ed.
*
SM 7 Online
..............................
..............................
.............................
..............................
3120 B ..............................
..........................................
..........................................
4110 B ..............................
3120
3113
3111
4110
4500–Cl– D .......................
4500–Cl– B .......................
4500–Cl– D .......................
4500–Cl– B .......................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
.........................
D4327–97, 03
2120
5540
3120
3111
3113
3120
3111
3113
2150
3120
3111
3113
4110
2120 B ..............................
5540 C .............................
3120 B ..............................
..........................................
..........................................
3120 B ..............................
..........................................
..........................................
2150 B ..............................
3120 B ..............................
..........................................
..........................................
4110 B ..............................
2120
5540
3120
3111
3113
3120
3111
3113
2150
3120
3111
3113
4110
.........................
4500–SO4 2– F .................
4500–SO4 2– C, D ............
4500–SO4 2– E .................
2540 C .............................
3120 B ..............................
3111 B ..............................
2540 C .............................
3120 B ..............................
..........................................
Other
4500–SO4 2– F.
4500–SO4 2– C, D.
4500–SO4 2– E.
.........................
.........................
.........................
*
4500–Cl– D–97.
4500–Cl– B–97.
D512–89 (Reapproved
1999) B.
3120
3113
3111
4110
*
D516–90, 02 ...
2. Chloride ........................
200.8 2
200.9 2
300.0 1,
300.1 6
.........................
.........................
.........................
D4327–97, 03
§ 143.4
B–99.
B–99.
D–99.
B–00.
D6508, Rev. 2 8
3. Color .............................
4. Foaming Agents ...........
5. Iron ...............................
................
................
200.7 2
200.9 2
6. Manganese ...................
200.7 2
200.8 2
200.9 2
7. Odor ..............................
8. Silver .............................
9. Sulfate ..........................
200.7 2
200.8 2
200.9 2
300.0 1,
300.1 6
375.2 1
B
C
B
B
B
B
B
B
B
B
B
B
B
..............................
.............................
..............................
..............................
..............................
..............................
..............................
..............................
..............................
..............................
..............................
..............................
..............................
B–01.
C–00.
B–99.
B–99.
B–99.
B–99.
B–99.
B–99.
B–97.
B–99.
B–99.
B–99.
B–00.
I–3720–85 5
D6508, Rev. 2 8
10. Total Dissolved Solids
11. Zinc .............................
200.7 2
200.8 2
2540 C–97.
3120 B–99.
3111 B–99.
The procedures shall be done in accordance with the documents listed below. The incorporation by reference of the following documents 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 below. Information regarding obtaining these documents can
be obtained from the Safe Drinking Water Hotline at 800–426–4791. Documents may be inspected at EPA’s Drinking Water Docket, EPA West, 1301 Constitution Avenue, NW., Room 3334,
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.
1 ‘‘Methods for the Determination of Inorganic Substances in Environmental Samples,’’ EPA/600/R–93–100, August 1993. Available at NTIS, PB94–120821.
2 ‘‘Methods for the Determination of Metals in Environmental Samples—Supplement I,’’ EPA/600/R–94–111, May 1994. Available at NTIS, PB 95–125472.
3 Annual Book of ASTM Standards, 1994, 1996, 1999, or 2004, Vols. 11.01 and 11.02, ASTM International; any year containing the cited version of the method may be used. Copies may
be obtained from the ASTM International, 100 Barr Harbor Drive, West Conshohocken, PA 19428.
4 Standard Methods for the Examination of Water and Wastewater, 18th edition (1992), 19th edition (1995), or 20th edition (1998). American Public Health Association, 1015 Fifteenth
Street, NW., Washington, DC 20005. The cited methods published in any of these three editions may be used, except that the versions of 3111 B, 3111 D, and 3113 B in the 20th edition
may not be used.
5 Method I–3720–85, Techniques of Water Resources Investigation of the U.S. Geological Survey, Book 5, Chapter A–1, 3rd ed., 1989. Available from Information Services, U.S. Geological
Survey, Federal Center, Box 25286, Denver, CO 80225–0425.
6 ‘‘Methods for the Determination of Organic and Inorganic Compounds in Drinking Water,’’ Vol. 1, EPA 815-R–00–014, August 2000. Available at NTIS, PB2000–106981.
7 Standard Methods Online are available at https://www.standardmethods.org. The year in which each method was approved by the Standard Methods Committee is designated by the last
two digits in the method number. The methods listed are the only online versions that may be used.
8 Method D6508, Rev. 2, ‘‘Test Method for Determination of Dissolved Inorganic Anions in Aqueous Matrices Using Capillary Ion Electrophoresis and Chromate Electrolyte,’’ available from
Waters Corp, 34 Maple St., Milford, MA, 01757, Telephone: 508/482–2131, Fax: 508/482–3625.
PART 430—THE PULP, PAPER, AND
PAPERBOARD POINT SOURCE
CATEGORY
19. The authority citation for part 430
continues to read as follows:
I
Authority: Sections 301, 304, 306, 307,
308, 402, and 501 of the Clean Water Act, as
amended, (33 U.S.C. 1311, 1314, 1316, 1317,
1318, 1342, and 1361), and Section 112 of the
Clean Air Act, as amended (42 U.S.C. 7412).
20. Section 430.02 is amended by
adding paragraph (g) to read as follows:
I
rwilkins on PROD1PC63 with RULES
§ 430.02
Monitoring requirements.
*
*
*
*
*
(g) Analyst may use NCASI Method
CP–86.07, ‘‘Chlorinated Phenolics in
Water by In situ Acetylation and GC/MS
Determination’’ (January 2002) for
determination of certain chlorinated
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phenols, chlorinated guaiacols,
chlorinated catechols, chlorinated
benzaldehydes (i.e., vanillins and
syringaldehydes), and trichlorsyringol
(analytes specified in the method) in
bleach plant filtrate as an alternative to
EPA Method 1653. NCASI Method CP–
86.07 is available from the Publications
Coordinator, NCASI, P.O. Box 13318,
Research Triangle Park, NC 27709–3318.
Telephone: 919–588–1987.
PART 455—PESTICIDE CHEMICALS
21. The authority citation for Part 455
continues to read as follows:
I
Authority: Secs. 301, 304, 306, 307, and
501, Pub. L. 92–500, 86 Stat. 816, Pub. L. 95–
217, 91 Stat. 156, and Pub. L. 100–4 (33
U.S.C. 1311, 1314, 1316, 1317, 1361).
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22. Section 455.50 is revised to read
as follows:
I
§ 455.50
Identification of test procedures.
The pesticide active ingredients to
which this section applies and for
which effluent limitations guidelines
and standards are specified in this Part
are named, together with the Chemical
Abstracts Service (CAS) number
(provided to assist in identifying the
pesticide active ingredient only) and
analytical method(s) designation(s) in
Table IG at 40 CFR 136.3(a). Except as
provided in 40 CFR 136.5, the discharge
parameter values required under the
Clean Water Act must be determined by
one of the analytical methods cited and
described in Table IG at 40 CFR
136.3(a). Pesticide manufacturers may
not use the analytical method cited in
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Table IB, Table IC, or Table ID of 40 CFR
136.3(a) to make these determinations
(except where the method cited in those
tables is identical to the method
specified in Table IG at 40 CFR
136.3(a)). The full texts of the analytical
methods cited in Table IG at 40 CFR
136.3(a) are contained in the Methods
For The Determination of
Nonconventional Pesticides In
Municipal and Industrial Wastewater,
Volume I, EPA 821-R–93–010A (August
1993 Revision I) and Volume II, EPA
821-R–93–010B (August 1993) (the
‘‘Compendium’’). Each pesticide
chemical manufacturer that is required
to determine discharge parameter values
under this Part using one of the
analytical methods cited in Table IG at
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40 CFR 136.3(a) must request in writing
a copy of the Compendium from the
permit authority or local control
authority (as applicable) prior to
determining such discharge parameter
values, unless the manufacturer already
has a copy.
I 23. Part 455 is amended by removing
and reserving Table 7 to Part 455.
PART 465—COIL COATING POINT
SOURCE CATEGORY
24. The authority citation for Part 465
continues to read as follows:
I
Authority: Secs. 301,304 (b), (c), (e), and
(g), 306 (b) and (c), 307 (b) and (c), and 501
of the Clean Water Act (the Federal Water
Pollution Control Act of 1972, as amended by
the Clean Water Act of 1977)(the ‘‘Act’’); 33
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11249
U.S.C. 1311, 1314 (b), (c), (e), and (g), 1316
(b) and (c), 1317 (b) and (c), and 1361; 86
Stat. 816, Pub. L. 92–500; 91 Stat. 1567, Pub.
L. 95–217.
25. Section 465.03 is amended by
revising paragraph (c) to read as follows:
I
§ 465.03 Monitoring and reporting
requirements.
*
*
*
*
*
(c) The analytical method required for
determination of petroleum
hydrocarbons (non-polar material) is
given under the listing for ‘‘oil and
grease’’ at 40 CFR 136.3(a), Table IB and
must be used after December 31, 2005.
*
*
*
*
*
[FR Doc. 07–1073 Filed 3–9–07; 8:45 am]
BILLING CODE 6560–50–P
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[Federal Register Volume 72, Number 47 (Monday, March 12, 2007)]
[Rules and Regulations]
[Pages 11200-11249]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: 07-1073]
[[Page 11199]]
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Part III
Environmental Protection Agency
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40 CFR Part 122, 136, et al.
Guidelines Establishing Test Procedures for the Analysis of Pollutants
Under the Clean Water Act; National Primary Drinking Water Regulations;
and National Secondary Drinking Water Regulations; Analysis and
Sampling Procedures; Final Rule
Federal Register / Vol. 72, No. 47 / Monday, March 12, 2007 / Rules
and Regulations
[[Page 11200]]
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ENVIRONMENTAL PROTECTION AGENCY
40 CFR Parts 122, 136, 141, 143, 430, 455, and 465
[EPA-HQ-OW-2003-0070; FRL-8203-8]
RIN 2040-AD71
Guidelines Establishing Test Procedures for the Analysis of
Pollutants Under the Clean Water Act; National Primary Drinking Water
Regulations; and National Secondary Drinking Water Regulations;
Analysis and Sampling Procedures
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This rule modifies the testing procedures approved for
analysis and sampling under the Clean Water Act and Safe Drinking Water
Act. EPA proposed these changes for public comment on August 18, 2003
and April 6, 2004. The Clean Water Act changes adopted in this final
rule fall into the following categories: new vendor-developed methods
as well as EPA and voluntary consensus standard bodies (VCSB) methods,
updated versions of currently approved methods, revisions to method
modification and analytical requirements, withdrawal of certain
outdated methods, and changes to sample collection, preservation, and
holding time requirements. This rule also changes regulations under the
Safe Drinking Water Act that establish drinking water sampling and
analysis procedures. The changes include approval of vendor-developed
methods, new EPA and VCSB methods, updated VCSB methods, and approval
of a modification to the test kit used with Syngenta Method AG-625 that
restricts its use in certain circumstances. The addition of new and
updated methods to the wastewater and drinking water regulations
provides increased flexibility to the regulated community and
laboratories in the selection of analytical methods.
ADDRESSES: EPA has established a docket for this action under Docket ID
No. EPA-OW-2003-0070. All documents in the docket are listed on the
https://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 https://
www.regulations.gov or in hard copy at the HQ Water Docket Center, EPA/
DC, EPA West, Room 3334, 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 for the HQ Water Docket Center.
DATES: This regulation is effective April 11, 2007. The incorporation
by reference of these methods is approved by the Director of the
Federal Register on April 11, 2007. For judicial review purposes, this
final rule is promulgated as of 1:00 p.m. (Eastern time) on March 26,
2007 as provided at 40 CFR 23.2 and 23.7.
FOR FURTHER INFORMATION CONTACT: For information regarding the changes
to wastewater regulations, contact Meghan Hessenauer, Engineering and
Analysis Division (4303T), USEPA Office of Science and Technology, 1200
Pennsylvania Ave., NW., Washington, DC 20460, 202-566-1040 (e-mail:
hessenauer.meghan@epa.gov). For information regarding the changes to
drinking water regulations, contact Patricia Snyder Fair, Technical
Support Center (MS 140), USEPA, Office of Ground Water and Drinking
Water, 26 West Martin Luther King Drive, Cincinnati, OH 45268, 513-569-
7937 (e-mail: fair.pat@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, the
NPDES permittee must use an approved test procedure (or an approved
alternate test procedure) for the specific pollutant when measuring the
required waste constituent. Similarly, if EPA has established sampling
requirements, measurements taken 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 regulated
Category entities
------------------------------------------------------------------------
State, Territorial, and Indian States, Territories, and Tribes
Tribal 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.
2. Safe Drinking Water Act
Public water systems are the regulated entities required to measure
contaminants in drinking water samples. In addition, EPA Regions, as
well as States, and Tribal governments with authority to administer the
regulatory program for public water systems under the Safe Drinking
Water Act, may also measure contaminants in water samples. When EPA
establishes a maximum contaminant level (MCL) for a given drinking
water contaminant, the Agency also approves standardized test
procedures for analysis of the contaminant. Public water systems
required to test water samples must use
[[Page 11201]]
one of the approved test procedures. Categories and entities that may
ultimately be subject to the requirements of today's rule include:
------------------------------------------------------------------------
Examples of potentially
Category regulated entities NAICS \1\
------------------------------------------------------------------------
State, Local, & Tribal States, local and tribal 924110
Governments. governments that
analyze water samples
on behalf of public
water systems required
to conduct such
analysis; States, local
and tribal governments
that themselves operate
community and non-
transient non-community
water systems required
to monitor.
Industry......................... Private operators of 221310
community and non-
transient non-community
water systems required
to monitor.
Municipalities................... Municipal operators of 924110
community and non-
transient non-community
water systems required
to monitor.
------------------------------------------------------------------------
\1\ North American Industry Classification System.
This table is not intended to be exhaustive, but rather provides a
guide for readers regarding entities likely to be regulated by this
action. The 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 141.2 (definition of public water
system). 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.
B. 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
March 26, 2007 as provided at 40 CFR 23.2. Under section 1448 (a) of
the Safe Drinking Water Act (SDWA), judicial review of today's SDWA
rule may be obtained by filing a petition for review only in the United
States Court of Appeal for the District of Columbia Circuit within 45
days from the date of promulgation of this rule. For SDWA judicial
review purposes, this final rule is promulgated as of 1 p.m. (Eastern
time) on March 26, 2007 as provide at 40 CFR 23.7. The requirements of
this regulation may also not be challenged later in civil or criminal
proceedings brought by EPA.
C. Abbreviations and Acronyms Used in the Preamble and Final Rule
AOAC: AOAC-International
ASTM: ASTM International
ATP: Alternate Test Procedure
CWA: Clean Water Act
EPA: Environmental Protection Agency
FLAA: Flame Atomic Absorption Spectroscopy
ICP-AES: Inductively Coupled Plasma-Atomic Emission Spectroscopy
ICP-MS: Inductively Coupled Plasma-Mass Spectroscopy
NPDES: National Pollutant Discharge Elimination System
NPDWR: National Primary Drinking Water Regulations
NSDWR: National Secondary Drinking Water Regulations
QC: Quality Control
SDWA: Safe Drinking Water Act
STGFAA: Stabilized Temperature Graphite Furnace Atomic Absorption
Spectroscopy
USGS: United States Geological Survey
VCSB: Voluntary Consensus Standard Body
D. Table of Contents
I. Statutory Authority
A. Clean Water Act
B. Safe Drinking Water Act
II. Summary of Final Rule
A. 40 CFR Part 122
B. 40 CFR Part 136
C. 40 CFR Parts 141 and 143
D. 40 CFR Part 430
E. 40 CFR Part 455
F. 40 CFR Part 465
III. Changes Between the Proposed Rule and the Final Rule
A. Silver Determinations
B. ASTM Method D5673-02 ``Standard Test Method for Elements in
Water by Inductively Coupled Plasma--Mass Spectrometry''
C. Ammonia Determinations
D. Available Cyanide Determinations
E. Kelada-01 Method for Determination of Available Cyanide and
Total Cyanide
F. Mandatory Replacement of Mercuric Sulfate with Copper Sulfate
in Methods for Determination of Total Kjeldahl Nitrogen
G. Approval of Additional Standards for Turbidity Determinations
H. Allowed Use of Capillary Columns in EPA Methods 601-613, 624,
625, and 1624B
I. Changes to Sampling Requirements at 40 CFR Parts 122, 136,
and 403
J. Approval Status of Total Elements Digestion
K. EPA Method 245.7 for Determination of Mercury
L. Clarification of Reporting Requirements
M. Corrections to 40 CFR Part 136, Tables IA, IB, IC, ID, IE and
Footnotes
N. Revisions to 40 CFR Part 136, Table II
O. Corrections to Tables 40 CFR 141.23, 141.24, 141.25, and
141.74 and Footnotes
P. Retention of Syngenta Method AG-625 for Determination of
Atrazine
Q. EPA Method 327.0 for Determination of Chlorine Dioxide
R. Deferral of Action on Microtox[supreg] 1010
IV. Response to Comments
A. Use of Syngenta Method AG-625 for Determination of Atrazine
B. Results From Use of Revised Methods, ``The Determination of
Radium-226 and Radium-228 in Drinking Water by Gamma-ray
Spectrometry Using HPGE or Ge(Li) Detectors.'' (Revision 1.2,
December 2004)
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
A. 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
[[Page 11202]]
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).
B. Safe Drinking Water Act
The Safe Drinking Water Act (SDWA), as amended in 1996, requires
EPA to promulgate national primary drinking water regulations (NPDWRs)
that specify maximum contaminant levels (MCLs) or treatment techniques
for drinking water contaminants (SDWA section 1412 (42 U.S.C. 300g-1)).
NPDWRs apply to public water systems pursuant to SDWA sections
1401(1)(A) (42 U.S.C. 300f(1)(A)). According to SDWA section
1401(1)(D), NPDWRs include ``* * * criteria and procedures to assure a
supply of drinking water which dependably complies with such maximum
contaminant levels; including accepted methods for quality control and
testing procedures * * *'' (42 U.S.C. 300f(1)(D)). In addition, SDWA
section 1445(a) authorizes the Administrator to establish regulations
for monitoring to help determine whether persons are acting in
compliance with the requirements of the SDWA (42 U.S.C. 300j-4). EPA's
promulgation of analytical methods for NPDWRs is authorized under these
sections of the SDWA as well as the general rulemaking authority in
SDWA section 1450(a) (42 U.S.C. 300j-9(a)).
The SDWA also authorizes EPA to promulgate national secondary
drinking water regulations (NSDWRs) for contaminants in drinking water
that primarily affect the aesthetic qualities relating to the public
acceptance of drinking water (SDWA section 1412 (42 U.S.C. 300g-1)).
These regulations are not Federally enforceable but are guidelines for
the States (40 CFR 143.1). The NSDWRs also include analytical
techniques for determining compliance with the regulations (40 CFR
143.4). EPA's promulgation of analytical methods for NSDWRs is
authorized under general rulemaking authority in SDWA section 1450(a)
(42 U.S.C. 300j-9(a)).
II. Summary of Final Rule
The following sections describe the changes EPA is making in
today's final rule.
A. 40 CFR Part 122
1. Some EPA Effluent Guideline regulations, as well as EPA's Sewage
Sludge Use and Disposal Regulations, require the use of analytical
methods specifically prescribed by the Guideline (see e.g. 40 CFR Part
420.21(c)). This rule amends the National Pollutant Discharge
Elimination System (NPDES) regulations at 40 CFR Part 122 to clarify
when an NPDES permittee must use for its monitoring and reporting the
analytical methods specifically required in Title 40 of the CFR,
Chapter I, Subchapters N and O (effluent guidelines and sewage sludge,
respectively) rather than the methods in 40 CFR Part 136. The
regulatory language has been amended to explicitly require either use
of methods at 40 CFR Part 136, or other methods that are specifically
prescribed for the particular wastestream or for sewage sludge
monitoring requirements.
2. The rule also corrects inconsistencies in sampling requirements
by referencing back to 40 CFR Part 136 to explicitly require use of
procedures at 40 CFR Part 136.
3. Sections 122.21(g)(7), 122.21(h)(4)(i), and 122.21(j)(4)(viii)
require an NPDES permit applicant to report quantitative data for
certain pollutants. The rule adds E. coli and Enterococci to the list
of parameters at 40 CFR 122.21(g)(7) and 122.21(h)(4)(i), and adds E.
coli to the list of parameters at 40 CFR 122.21(j)(4)(viii).
B. 40 CFR Part 136
This rule approves new and revised methods for inclusion in 40 CFR
Part 136. Many of those methods are from the voluntary consensus
standards body (VCSB) that publishes Standard Methods for the
Examination of Water and Wastewater. Those ``Standard Methods'' are now
available in both hard copy and electronic formats. The publisher
identifies Standard Methods in two ways, depending on the medium of
publication. Hard copy methods are identified by the method number
(e.g., SM 4500-Cl E) and the edition of the manual in which they appear
(e.g., 18th, 19th, 20th Editions), while the electronic versions
available on-line are identified by the same method number and the year
the method was approved for release (e.g., 4500-Cl E-00).
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
three new methods submitted as alternate test procedures for monitoring
chemical pollutants. These methods are ``Test Method for Determination
of Dissolved Inorganic Anions in Aqueous Matrices Using Capillary Ion
Electrophoresis and Chromate Electrolyte'' (D6508, Rev. 2) by Waters
Corporation, ``Digestion and Distillation of Total Cyanide in Drinking
and Wastewaters using MICRO DIST and Determination of Cyanide by Flow
Injection Analysis'' (QuikChem Method 10-204-00-1-X) by Lachat
Instruments, and ``Kelada Automated Test Methods for Total Cyanide,
Acid Dissociable Cyanide, and Thiocyanate'' (Kelada-01) by Dr. Nabih
Kelada.
2. The rule approves a broad purpose digestion procedure for total
recoverable elements digestion. EPA is approving EPA Method 200.2
(Revision 2.8, 1994) for use with Inductively Coupled Plasma-Atomic
Emission Spectroscopy (ICP-AES), Inductively Coupled Plasma-Mass
Spectroscopy (ICP-MS), Stabilized Temperature Graphite Furnace Atomic
Absorption (STGFAA), and Flame Atomic Absorption Spectroscopy (FLAA)
methods.
3. The rule approves three new multi-element test procedures. The
approved methods are EPA Method 200.8 (Revision 5.4, 1994), AOAC Method
993.14 [16th Edition], and ASTM D5673-03 for determination of elements
by ICP-MS.
4. EPA is also approving a new multi-element test procedure, EPA
Method 200.9 (Revision 2.2, 1994), for determination of elements by
STGFAA.
5. The rule approves four new methods for determination of
hexavalent chromium by ion chromatography. The methods are EPA Method
218.6, AOAC Method 993.23 [16th Edition], and ASTM D5257-97--SM 3500-Cr
C [20th Edition] and SM 3500-Cr E [18th, 19th Editions].
6. The rule approves five new methods for determination of anions
by ion chromatography. The methods are EPA Method 300.0 (Revision 2.1,
1993), EPA Method 300.1 (Revision 1.0, 1997), AOAC Method 993.30 [16th
Edition], ASTM D4327, and SM 4110 B [18th, 19th, and 20th Editions].
7. The rule approves the use of six automated cadmium reduction
methods to determine nitrate and nitrite individually, as well as in
combination. The methods are EPA Method 353.2 (Revision 2.0, 1993),
ASTM D3867-99 (A) and (B), SM 4500-NO3-E and F
[18th, 19th, 20th Editions] and 4500-NO3-E and F
(2000), and USGS Method I-4545-85.
8. The rule approves a new method for determination of chlorine by
low level amperometry--SM 4500-Cl E [18th, 19th, 20th Editions] and SM
4500-Cl E (2000).
[[Page 11203]]
9. The rule replaces EPA Method 180.1 (1978) for determination of
turbidity with EPA Method 180.1 (Revision 2.0, 1993).
10. The rule replaces EPA Method 200.7 (1990) for determination of
elements by ICP-AES with EPA Method 200.7 (Revision 4.4, 1994).
11. The rule replaces EPA Method 245.1 (1974) for determination of
mercury with EPA Method 245.1 (Revision 3.0, 1994).
12. The rule replaces EPA Method 335.3 (1978) for determination of
total cyanide with EPA Method 335.4 (Revision 1.0, 1993) with a
footnote to clarify the proper procedure for removing sulfide
interferences.
13. The rule replaces EPA Method 350.1 (1978) for determination of
ammonia with EPA Method 350.1 (Revision 2.0, 1993).
14. The rule replaces EPA Method 351.2 (1978) for determination of
total Kjeldahl nitrogen (TKN) with EPA Method 351.2 (Revision 2.0
1993).
15. The rule replaces EPA Method 353.2 (1978) for determination of
nitrate-nitrite with EPA Method 353.2 (Revision 2.0, 1993).
16. The rule replaces EPA Method 365.1 (1978) for determination of
phosphorus (all forms) with EPA Method 365.1 (Revision 2.0, 1993).
17. The rule replaces EPA Method 375.2 (1978) for determination of
sulfate with EPA Method 375.2 (Revision 2.0, 1993).
18. The rule replaces EPA Method 410.4 (1978) for determination of
chemical oxygen demand (COD) with EPA Method 410.4 (Revision 2.0,
1993).
19. The rule replaces EPA Method 420.2 (1974) for determination of
total phenols with EPA Method 420.4 (Revision 1.0, 1993).
20. The rule approves a new method for the determination of
mercury, EPA Method 245.7 ``Mercury in Water by Cold Vapor Atomic
Fluorescence Spectrometry'' [Revision 2.0, 2005] (EPA-821-R-05-001).
21. The rule approves a new method for determination of available
cyanide by ligand exchange followed by flow injection analysis, ASTM
D6888-04.
22. The rule approves a new method for determination of cations by
ion chromatography, ASTM D6919-03.
23. The rule approves a new method for determination of chloride by
potentiometry, SM 4500-Cl-D [18th, 19th, 20th Editions] and
SM 4500-Cl-D (2000).
24. The rule approves a new method for determination of chloride by
ion selective electrode, ASTM D512-89 (1999).
25. The rule approves two new methods for determination of total
cyanide by ion selective electrode, SM 4500-CN-F [18th,
19th, 20th Editions] and SM 4500-CN-F (2000), and ASTM
D2036-98 A.
26. The rule approves two new methods for determination of sulfide
by ion selective electrode, SM 4500-S2-G [18th,
19th, 20th Editions] and ASTM D4658-03 (1996).
27. The rule approves a new method for determination of nitrate by
ion selective electrode, SM 4500-NO3-[18th, 19th,
20th Editions] and SM 4500-NO3-(2000).
28. The rule approves an errata sheet to correct typographical
errors in the following methods manuals, ``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 (the
``freshwater chronic manual''), and ``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 (the ``freshwater
acute manual'').
29. The rule approves the use of newer versions of 74 methods
published by ASTM International. The new versions are published in the
1994, 1996, and 1999 Annual Book of ASTM Standards Vols. 11.01 and
11.02, in the 2000 Annual Book of ASTM Standards, Vol. 11.02 and in
individual standards published after 2000.
30. The rule approves the use of newer versions of 88 methods
published by the Standard Methods Committee and adopts a new numbering
system to track the approved versions of Standard Methods. The new
versions are published in Standard Methods Online (APHA 2003).
31. The rule approves the use of newer versions of 19 methods
published by AOAC-International. The new versions of these methods are
published in Official Methods of Analysis of AOAC-International, 16th
Edition, 1995.
32. The rule approves the replacement of the mercuric sulfate
catalyst with copper sulfate in methods approved for the determination
of total Kjeldahl nitrogen (TKN).
33. The rule approves the use of styrene divinyl benzene beads and
stabilized formazin as alternatives to the presently approved formazin
standard for determination of turbidity.
34. As described in the preamble to the April 2004 proposed rule
(69 FR 18213), EPA is adopting a new Sec. 136.6 to introduce greater
flexibility in the use of approved methods. The section describes the
circumstances in which approved methods may be modified and the
requirements that analysts must meet to use these modified methods in
required measurements without prior EPA approval. The rule also
includes language at Sec. 136.6(c) to clarify that analysts need only
meet method performance requirements for target analytes (those
analytes being measured for NPDES reporting) when using multi-analyte
methods for compliance monitoring purposes. The rule also includes the
language at Sec. 136.6(d) to allow explicitly the use of capillary
(open tubular) GC columns with EPA Methods 601-613, 624, 625, and 1624B
as alternatives to the packed GC columns specified in those methods,
provided that analysts generate new retention time tables with
capillary columns to be kept on file with other information for review
by auditors.
35. The rule withdraws 109 methods contained in EPA's ``Methods for
the Chemical Analysis of Water and Wastes'' for which approved
alternatives published by voluntary consensus standards bodies (e.g.,
ASTM and Standard Methods) are available.
36. The rule withdraws liquid-liquid extraction (LLE) methods,
including EPA Methods 612 and 625, as approved procedures for
determination of 1,2-dichlorobenzene, 1,3-dichlorobenzene, and 1,4-
dichlorobenzene.
37. The rule withdraws approval of all oil and grease methods that
use chlorofluorocarbon-113 (CFC-113; Freon-113) as an extraction
solvent.
38. The rule revises Table II (Required Containers, Preservation
Techniques, and Holding Times) and the footnotes to the table at 40 CFR
136.3(e). The table and footnotes specify approved sampling,
preservation, and holding time requirements for the methods approved
for compliance monitoring to reduce confusion, resolve any conflicts
with instructions in the underlying compliance monitoring method, and
reflect current understanding of sample preservation requirements. The
most significant of the changes are those made to Footnote 6, which
addresses the preservation of samples to be analyzed for cyanide. Based
on information gathered during the development of new cyanide methods
approved in this rulemaking, and information collated from various
commenters and experts in cyanide analyses, EPA revised footnote 6 to
Table II by adding text that describes procedures that are recommended
for removal or suppression of cyanide interferences, including
interferences
[[Page 11204]]
from sulfur, sulfide, sulfite, thiocyanate, and aldehydes. The
recommended procedures may differ from those described in the older
approved methods.
39. EPA is changing ``Director of the Environmental Monitoring
Systems Laboratory'' and ``Director, Analytical Methods Staff'' to
``Alternate Test Procedure Program Coordinator, Washington, DC'' every
place the phrases appear in the regulations. This reflects the current
organizational structure and title for the head of EPA's Alternate Test
Procedure (ATP) Program management. In addition, addresses for
submission of ATPs are being updated to reflect the current location of
the Alternate Test Procedure Program Coordinator.
40. The rule makes other minor editorial revisions to clarify
existing regulations.
C. 40 CFR Parts 141 and 143
1. This rule amends the regulations at 40 CFR Part 141 and Part 143
to allow the use of 66 methods in ''Standard Methods Online'' (APHA
2003) (40 CFR 141.21, 141.23, 141.74, and 143.4).
2. This rule allows the use of 28 newer versions of methods
published by ASTM International. The new versions are published in the
1999 ``Annual Book of ASTM Standards,''' Vols.11.01 and 11.02, in the
2000 ``Annual Book of ASTM Standards,'' Vol. 11.02 and in individual
standards published after 2000 (40 CFR 141.23).
3. This rule approves a new method submitted as an alternate test
procedure for the determination of common anions--chloride, fluoride,
nitrate, nitrite, orthophosphate, and sulfate, ``Test Method for
Determination of Dissolved Inorganic Anions in Aqueous Matrices Using
Capillary Ion Electrophoresis and Chromate Electrolyte'' (D6508, Rev.
2) by Waters Corporation (40 CFR 141.23 and 143.4).
4. This rule approves two new methods for determination of
available cyanide, ``Available Cyanide by Flow Injection, Ligand
Exchange, and Amperometry,'' Method OIA-1677, DW (January 2004), and
ASTM D6888-04 (40 CFR 141.23).
5. This rule approves the use of EPA Method 300.1 (Revision 1.0,
1997) for compliance determinations of chloride, fluoride, nitrate,
nitrite, orthophosphate, and sulfate (40 CFR 141.23 and Sec. 143.4).
6. This rule approves the use of EPA Method 552.3 (Revision 1.0,
2003) for compliance determinations of dalapon (40 CFR 141.24).
7. This rule amends 40 CFR 141.25 to add a new method for
determination of radium-226 and radium-228. This method, ``The
Determination of Radium-226 and Radium-228 in Drinking Water by Gamma-
ray Spectrometry Using HPGE or Ge(Li) Detectors'' (Revision 1.2,
December 2004), was developed by the Environmental Resources Center at
the Georgia Institute of Technology, and was originally submitted to
EPA as an alternate test procedure to the currently approved methods
for determination of radium-226 and radium-228.
8. This rule allows States the option of approving ITS Free
chlorine test strips as a test kit for the measurement of free chlorine
using ``Free Chlorine Species'' (HOCl- and OCl-) by Test Strip,'' ITS
Method D99-003 (Revision 3.0, November 21, 2003) by Industrial Test
Systems, Inc. (40 CFR 141.74).
9. This rule approves EPA Method 327.0 (Revision 1.1, 2005) for
measurement of chlorine dioxide residuals (40 CFR 141.74).
10. This rule approves the use of styrene divinyl benzene beads and
stabilized formazin as alternatives to the presently approved formazin
standard for determination of turbidity (40 CFR 141.74).
11. This rule revises footnote 17 to the table at 40 CFR 141.23 to
allow the use of a 450-W UV lamp in the Kelada Method-01 for
determination of cyanide.
12. This rule allows the use of Syngenta Method AG-625, with the
modified immunoassay testing product manufactured by Beacon Analytical
Systems, for the measurement of atrazine under certain conditions. It
may only be used by those systems that do not use chlorine dioxide for
drinking water treatment. In addition, the results of the analysis of
samples with concentrations of atrazine more than one-half the atrazine
MCL (i.e., more than 1.5 [mu]g/L) must be confirmed using another
approved method (40 CFR 141.24).
13. This rules also revises footnote 8 to the table in paragraph
(a)(1) to correct a long-standing discrepancy between the footnote and
the specifications in Standard Method 9221 E. The table in question
lists Standard Method 9221 E as one of two procedures that may be used
for monitoring fecal coliforms. Footnote 8 simply notes the holding
time for the A-1 broth used in this procedure. Today's action corrects
the holding time specified in the footnote 8 to match the 7-day holding
time that is specified in Standard Method 9221 E (40 CFR 141.74)
D. 40 CFR Part 430
This rule amends the Effluent Limitations Guidelines for the pulp,
paper, and paperboard point source category at 40 CFR Part 430 to
approve a new method for determination of chlorinated phenolics in
wastewaters generated by these industries. The rule adds a new section,
430.02(g), to allow the use of ``Chlorinated Phenolics in Water by In
situ Acetylation and GC/MS Determination'' (Method CP-86.07) developed
by the National Council for Air and Stream Improvement (NCASI) as an
alternative to otherwise required Method 1653 in Part 430, Appendix A.
E. 40 CFR Part 455
This rule amends the regulations at 40 CFR Part 455 by moving Table
7 from 40 CFR Part 455 to 40 CFR Part 136.3(a) as new Table IG.
F. 40 CFR Part 465
This rule amends the Effluent Limitations Guidelines for the coil
coating point source category at 40 CFR Part 465 to replace the method
listed at section 465.03(c) for determination of oil and grease in
wastewater samples from all subcategories of coil coating with EPA
Method 1664A for determination of non-polar materials (NPM), which is
generally equivalent to total petroleum hydrocarbons.
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. Silver Determinations
EPA received comments on the Agency's proposed withdrawal of EPA
Method 272.1 which included information on how to keep silver in
solution in samples with known or suspected high levels of silver by
adding a solution containing cyanogen chloride. As a result, EPA has
added a footnote to Table IB at Sec. 136.3 to include procedures for
preparation and addition of this reagent to digested samples of this
type to keep the silver in solution for analysis by any of the approved
methods. The Agency is withdrawing EPA Method 272.1, as proposed in
April 2004 (69 FR 18183 April 6, 2004).
B. ASTM Method D5673-02 ``Standard Test Method for Elements in Water by
Inductively Coupled Plasma--Mass Spectrometry''
Based on comment received on the Agency's proposed approval of ASTM
Method D5673-02, EPA is approving an updated version of this method
ASTM D5673-03. EPA included the updated version of this method in a
notice of data availability (70 FR 7909, February 16, 2005) and
requested public
[[Page 11205]]
comment on whether it should be approved. EPA received no adverse
comments.
C. Ammonia Determinations
EPA received comment on the Agency's proposed approval of an
updated version of EPA Method 350.1. The commenter stated that
mandating the use of ethylene-diamine-tetra-acetate (EDTA) in the
method could adversely affect method performance when using an
automated analyzer and submitted data to support this claim. Based on
EPA's review of the data, the Agency is adding a footnote to Table IB
at Sec. 136.3 allowing analysts to omit EDTA from EPA Method 350.1,
provided that all of the quality control (QC) acceptance criteria in
the method are met.
D. Available Cyanide Determinations
The Agency solicited comment regarding problems encountered with
the use of ligand exchange-amperometric detection methods for
determination of available cyanide in samples that contain significant
amounts of solids and solicited potential solutions to these problems.
Based on public comment, EPA is adding a footnote to Table IB at Sec.
136.3 that includes suggestions for sample filtration and for limiting
the time between addition of ligand exchange reagents and analysis to
solve these problems when necessary. The Agency proposed ASTM Method
D6888-03 for determining available cyanide. Since publication of the
proposal, EPA has received a revised version of this method. EPA
included this revised version in a Notice of Data Availability (NODA)
and requested public comment on the approval of this revised version of
the method (70 FR 7909, February 16, 2005). D6888-04 contains a new
online sulfide removal procedure and represents a refinement to the
proposed version. EPA received no adverse comments on this revised
version of the method and is approving ASTM Method D6888-04 in today's
rule.
E. Kelada-01 Method for Determination of Available Cyanide and Total
Cyanide
Based on a comment and data received on the Agency's proposed
approval of the Kelada-01 method for determination of available cyanide
and total cyanide for use in NPDES compliance monitoring, a note has
been added at 40 CFR 136.3, Table IB, Footnote 55 to allow the use of
450-W UV lamp instead of the 550-W lamp specified in the method if it
provides performance within the quality control acceptance criteria of
the method in a given instrument. Similarly, modified flow cell
configurations and flow conditions may be used in the method, provided
that the QC acceptance criteria are met. The Agency also is adding the
note at 40 CFR 141.23, Footnote 17, as this method was previously
approved for use in drinking water compliance monitoring.
F. Mandatory Replacement of Mercuric Sulfate With Copper Sulfate in
Methods for Determination of Total Kjeldahl Nitrogen
The Agency proposed the mandatory replacement of mercury sulfate
with copper sulfate in total Kjeldahl nitrogen (TKN) digestion.
Comments expressed concern that copper sulfate will provide inferior
performance in some samples, and suggested that EPA allow the continued
use of mercury sulfate in analyses, offering copper sulfate as an
option. Based on EPA's evaluation of these comments, the Agency has
decided that it will continue to allow the use of mercury sulfate in
TKN analyses.
G. Approval of Additional Standards for Turbidity Determinations
Based on comments received on the proposed approval of additional
standards for use in methods to determine turbidity, the Agency is
replacing turbidity standard trade names with more generic listings in
the footnote to Table IB at Sec. 136.3. An example formulation for
each generic listing is also included in order to provide a reference
to at least one source of the generic standard material. The Agency
also is adding a similar footnote to the table in 40 CFR 141.74 where
the approved methods for the determination of turbidity in drinking
water are listed.
H. Allowed Use of Capillary Columns in EPA Methods 601-613, 624, 625,
and 1624B
The Agency proposed new language that explicitly allows the use of
capillary columns in place of packed columns with EPA Methods 601-613,
624, 625, and 1624B, provided that all QC tests in these methods are
performed and all QC acceptance criteria are met. Based on comments
received on this proposal, EPA is clarifying the regulations at Sec.
136.6 to state that retention times will change with the switch from
packed to capillary columns, so analysts are not required to meet the
retention times specified in the method when the switch is made.
Instead, analysts must generate new retention time tables with
capillary columns to be kept on file with other information for review
by auditors.
I. Changes to Sampling Requirements at 40 CFR Parts 122, 136, and 403
The Agency proposed changes to the sampling requirements specified
at 40 CFR Parts 122, 136 and 403. Based on comments received on these
proposed updates, the sampling requirements have been modified to
include clarifying language with respect to grab and composite sampling
requirements, and to add E. coli and Enterococci to the parameters
listed at Part 122.21 for which an NPDES applicant must provide
analytical information. In addition, on October 14, 2005, EPA published
in the Federal Register final changes to its General Pretreatment
Regulations (70 FR 60134). In these regulations, EPA consolidated
monitoring requirements for indirect dischargers into 40 CFR 403.12(g).
In the proposal for the current rule, EPA proposed to modify 40 CFR
403.12 (b). Based on changes made to 40 CFR Part 403 on October 14,
2005, however, the proposed modifications to CFR 403.12 (b) are no
longer required.
J. Approval Status of Total Elements Digestion
The Agency proposed to approve a ``total recoverable'' elements
digestion procedure, and also to retain ``total'' elements digestion
for graphite furnace atomic absorption (GFAA) analyses. Based on
comments received on this proposal, EPA is clarifying the language in
Table IB at Sec. 136.3 to specify Section 4.1.3 of Methods for
Chemical Analysis of Water and Wastes (MCAWW) as the approved digestion
procedure for use with non-platform graphite furnace atomic absorption
determinations.
K. EPA Method 245.7 for Determination of Mercury
The Agency proposed approval of EPA Method 245.7 (December 2003) as
an additional method for determination of mercury. Based on comments
received on this proposal, EPA has revised the method and is approving
EPA Method 245.7 (Revision 2.0, 2005) in this rule. Specifically, EPA
has approved the method with the following changes: includes a
discussion of the gas-liquid separator in Section 2.6, reduces the
amount of hydrochloric acid used during sample digestion, includes the
addition of hydrochloric acid (HCl) to standard solutions, clarifies
that additional procedures for handling difficult matrices may be used
provided that laboratories meet the method performance criteria, and
revises procedures for preparing reagent blanks to remove the addition
of stannous chloride (SnCl2) and include addition of
[[Page 11206]]
HCl. EPA also has corrected section numbering and references throughout
Sections 4 and 7 of the method.
L. Clarification of Reporting Requirements
The Agency proposed to add a new Sec. 136.7 that would clarify
that a quality control (QC) failure does not relieve a permittee of the
duty to report results and that results are to be reported to the level
specified in the method or required in the permit, whichever is lower.
EPA agrees with public comment that the proposed revision was unclear.
In this rule, EPA is revising this action to clarify our intent in text
at Sec. 136.3, rather than take final action on the proposed text at
Sec. 136.7.
EPA proposed a new Sec. 136.7 amendment to resolve conflicts
between current reporting requirements at 40 CFR Parts 122 and 125 and
preservation requirements at 40 CFR 136.3(e) and instructions in
compliance monitoring methods specified in the tables at 40 CFR
136.3(a). For example, some methods provide ``reject tests'' (e.g.
Method 5210 B 5-day BOD, section 6a, Standard Methods, 20th edition) or
state that a ``result may not be reported for regulatory compliance
purposes'' (e.g. Method OIA 1677: Available Cyanide, section 9.3.4, OI
Analytical) if an analytical quality control measure is outside its
control limit range (acceptance criteria). However, it may be necessary
to report such results if resampling, reanalysis or other corrective
action is not possible. Not reporting these results may cause a
permittee to be in violation of Part 122 or 125 reporting requirements.
Reporting such available data is recommended as a good laboratory
practice (D3856-95 Standard Guide for Good Laboratory Practices in
Laboratories Engaged in Sampling and Analysis of Water, Annual Book of
ASTM Standards, Water and Environmental Technology, Vol 11.01 Water
(I), p. 353, 2003).
For clarification, in this rule, EPA is adding a statement to the
text preceding Tables IA to IG at Sec. 136.3(a), and Table II at Sec.
136.3(e) to state that reporting requirements of Parts 122 or 125 may
take precedence over the otherwise applicable reporting or preservation
requirements of a particular analytical method.
M. Corrections to 40 CFR Part 136, Tables IA, IB, IC, ID, IE and
Footnotes
The Agency is correcting errors that were published in the proposed
Table IA (List of Approved Biological Methods), Table IB (List of
Approved Inorganic Test Procedures), Table IC (List of Approved Test
Procedures for Non-Pesticide Organic Compounds), Table ID (List of
Approved Test Procedures for Pesticides), and Table IE (List of
Approved Radiologic Test Procedures) and the footnotes to those tables.
N. Revisions to 40 CFR Part 136, Table II
The rule revises Table II (Required Containers, Preservation
Techniques, and Holding Times), and the footnotes to Table II at 40 CFR
136.3(e). The action of updating Table II at Sec. 136.3(e) reflects
EPA's evaluation of comments received on the April 6, 2004 proposal.
EPA revised footnote 1 to more clearly distinguish between polyethylene
(P), fluoropolymer (FP), glass (G), and low-density polyethylene (LDPE)
and has made it explicit that a sample to be used to determine fluoride
is to be collected in a polyethylene bottle. EPA revised footnotes 2
and 7 to add language to make more clear that preservation must be
within 15 minutes after collection of a grab sample, a composite
sample, or an aliquot split from a composite sample collected
automatically over time.
EPA modified footnote 4 to clarify the start of holding times for
the different types of sample collection (grab samples, composite
samples collected automatically, and a set of grab samples that is
composited in the laboratory). The revisions remove the requirement for
collection of samples to determine cyanide in amber glass bottles with
PTFE-lined caps from footnote 6. Footnotes 5 and 6 describe procedures
recommended for removal or suppression of cyanide interferences,
including interferences from oxidants, sulfide, sulfite, thiocyanate,
and aldehydes. In addition, the footnote also provides that other
procedures for removal or suppression of cyanide interferences may be
employed, provided the analyst demonstrates that such other procedures
more accurately measure cyanide.
EPA clarified requirements in footnote 17 specific to sampling for
trace mercury, added EPA Method 245.7 to footnote 17, and removed
footnote 17 from the ``Preservation'' and ``Maximum Holding Time''
headers. EPA has clarified footnote 18 to indicate that the number of
significant figures is intended to establish an absolute upper limit on
sample temperature and preclude meeting the specification through
rounding of numbers and added an exception to footnote 18 for a sample
analyzed immediately (in less than 15 minutes from collection). EPA
deleted footnote 19 because the information is now in footnote 5.
Deletion of this footnote resulted in renumbering all of the subsequent
footnotes to Table II.
EPA has also clarified that preservation is not required for soil
and sediment samples. EPA also has revised preservation requirements
for acrolein, acrylonitrile, and purgeable aromatics to remove
inconsistences, revised requirements for collection of samples to be
tested for Cryptosporidium and Giardia, and established 0-8 [deg]C as
the holding temperature for samples to be tested for Cryptosporidium.
In addition, the Agency is correcting minor formatting and
typographical errors that were published in the proposed Table II.
EPA recognizes that the requirements at Sec. 136.3 may differ from
those described in some older approved methods and today's action
clarifies that this section supersedes instructions in a compliance
method. Where there are conflicts with existing methods published by
EPA, VCSBs, or other entities, we expect that the next revisions of
these methods will conform to the requirements at Sec. 136.3(e).
O. Corrections to Tables 40 CFR Parts 141.23, 141.24, 141.25, and
141.74 and Footnotes
The final rule corrects a number of errors in the proposed tables
at Sec. 141.23 (Inorganic Chemical Sampling and Analytical
Requirements), 141.24 (Organic Chemicals, Sampling and Analytical
Requirements), 141.25 (Analytical Methods for Radioactivity) and 141.74
(Analytical and Monitoring Requirements) and the footnotes to those
tables. The Agency also revised the wording of several entries for the
cyanide methods in the tables at 40 CFR 141.23 to more clearly
distinguish among the various methodologies listed in those tables.
P. Retention of Syngenta Method AG-625 for Determination of Atrazine
The Agency proposed to withdraw approval of Syngenta Method AG-625
for the determination of atrazine in drinking water. Based on comments
received regarding the April 6, 2004 proposal and comments received
regarding additional data submitted in response to the Notice of Data
Availability (70 FR 7909, February 16, 2005), EPA has decided to retain
Syngenta Method AG-625 with some restrictions on its use. The revised
approval requires confirmation of any compliance monitoring results for
atrazine that are greater than one half of the MCL for atrazine, using
an alternate approved method. EPA based its approval on the use of the
modified immunoassay testing product produced
[[Page 11207]]
by Beacon Analytical Systems, the only version of the product that is
currently offered for sale. However, use is not authorized for public
water systems which use chlorine dioxide for drinking water treatment.
Q. EPA Method 327.0 for Determination of Chlorine Dioxide
The Agency proposed to approve EPA Method 327.0 (Revision 1.0,
2003) for the determination of chlorine dioxide (40 CFR 141.74). In the
final rule, the Agency has approved EPA Method 327.0 (Revision 1.1,
2005) and corrected three typographical errors in the proposed method.
R. Deferral of Action on Microtox[reg] 1010
Because EPA is continuing to evaluate public comment about use of
the Microtox[reg] 1010 test procedure for determinations of acute whole
effluent toxicity, and the data supporting use of this test procedure,
EPA is not taking final action on the proposal to approve Microtox[reg]
1010 for compliance monitoring.
IV. Response to Comments
EPA received two comments regarding methods included in this final
rule from the August 18, 2003 proposal (68 FR 49548), 115 comments on
the April 6, 2004 proposal (69 FR 18166), and nine comments on the
February 16, 2005 Notice of Data Availability (NODA) (70 FR 7909).
Commenters represented a number of different interests, including
analytical laboratories, water utilities, instrument manufacturers,
State and local governments, trade associations, scientists, and
private citizens. A summary of major public comments on the proposed
rules and the NODA and the Agency's responses is presented in this
section, and section III of this preamble. The public docket for this
rule includes the Agency's response to all comments.
A. Use of Syngenta Method AG-625 for Determination of Atrazine
EPA proposed withdrawing approval of Syngenta Method AG-625
(Syngenta Crop Protection Inc.) for the determination of atrazine.
Based on comments and additional data submitted in response to the
NODA, EPA has decided to retain Syngenta Method AG-625 as an approved
method for atrazine, subject to certain conditions. Today's amended
rule will require the use of an alternate approved method for atrazine
to confirm any results from the Syngenta method that are greater than
one half of the MCL for atrazine. EPA's decision to retain the approval
of Method AG-625 is based on using the modified immunoassay testing
product manufactured by Beacon Analytical Systems (Atrazine Plate Kit-
Cat CPP-004), the only version of the product currently
offered for sale. However, based on data submitted in response to the
NODA, EPA is not approving Method AG-625 for use when chlorine dioxide
is used for drinking water treatment.
One commenter supported the withdrawal of Syngenta Method AG-625,
citing EPA's Environmental Technology Verification (ETV) study, and
suggested that the method had not been validated adequately prior to
EPA's earlier approval. The commenter also suggested that approval of a
modified version of AG-625 may be preferable, but was concerned that
the method using the original testing product could lead to reports of
non-compliance and/or increased treatment cost based on erroneous
atrazine measurements in the interim.
Other comments questioned the validity of data submitted by the
American Water Works Association (AWWA) that demonstrated method
deficiencies and requested that the data not be considered by EPA. The
commenters noted that data were not accompanied by suitable quality
control checks and that some tests (i.e., testing the effect of humic
acid) were not reproducible in later studies by the same investigator.
The commenters also suggested that data generated by AWWA was not
generated according to Method AG-625, but rather by simply using the
commercial testing product without reference to the method.
As reported by Adams (Adams et al., JAWWA, 2004, pp. 126-139), the
original immunoassay test kit used with Method AG-625 was subject to a
positive bias in the measurement of atrazine in the presence of
disinfectants used in drinking water treatment, such as chlorine,
monochloroamine, chloramine T, chlorine dioxide and other substances.
Additionally, data reported by Adams using the modified Beacon test
kit, data from the Environmental Technology Verification (ETV) Program,
and, in fact, data in the December 2004 Syngenta study (Atrazine: Final
Report, Syngenta Number T006141-04, 12/10/2004), demonstrate that test
kits marketed by Beacon, Abraxis, and SDI show a modest positive bias
in raw and finished drinking water for most samples (i.e., the measured
concentrations in most samples were higher than the expected values).
For a distinct minority of samples in these two studies, no bias or a
negative bias was shown (i.e., the measured concentrations were equal
to or lower than the expected concentrations in a few samples). The
December 2004 Syngenta study submitted to EPA demonstrated that the
modified Beacon immunoassay test kit performed suitably in the presence
of chlorine, monochloroamine, chloramine T, chloroform, and humic acid.
However the data show that an interference occurred in the presence of
chlorine dioxide unless samples were analyzed within one day of
collection.
EPA agrees that data from both Syngenta and AWWA (Adams) indicate
that, except for cases involving chlorine dioxide, the modified testing
product performed substantially better with regard to the positive bias
and interferences than did the original product in the presence of
disinfectants and other interferences. EPA also agrees that, in
general, the immunoassay products examined in these studies exhibit
some positive bias for atrazine. Low results were only obtained from
analyses of a few samples.
EPA recognizes that a potential positive bias is a concern for
water utilities, particularly those located in areas such as the
Midwest, where atrazine is used extensively to control weeds in corn
and sorghum crops. However, in many other areas, where it is not used,
atrazine is not likely to be found in drinking water samples at all.
Because accurate information on the occurrence of contaminants at
concentrations close to the MCL is necessary for EPA to meet its
obligation to review MCLs every six years, EPA has retained approval of
Syngenta Method AG-625 for atrazine with the conditions on its use
described below. The following conditions have been added as Footnote 5
to the table at 40 CFR 141.24(e)(1).
``This method may not be used for the analysis of atrazine in
any system where chlorine dioxide is used for drinking water
treatment. In samples from all other systems, any result for
atrazine generated by Method AG-625 that is greater than one-half
the maximum contaminant level (MCL) (i.e., greater than 0.0015 mg/L
or 1.5 [mu]g/L) must be confirmed using another approved method for
this contaminant and should use additional volume of the original
sample collected for compliance monitoring. In instances where a
result from Method AG-625 triggers such confirmatory testing, the
confirmatory result is to be used to determine compliance.''
The MCL for atrazine is 0.003 mg/L (3 [mu]g/L). Thus, any results
from Method AG-625 greater than 0.0015 mg/L (1.5 [mu]g/L) must be
confirmed through the use of another approved method for atrazine. In
such instances, the
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confirmatory result is used to determine compliance, because the
methods used for confirmatory testing are considered more accurate.
EPA acknowledges that this requirement for confirmation may cause
some utilities to choose not to employ Method AG-625. However, the
approval of a method at 40 CFR Part 141 does not constitute a
requirement for its use when other approved methods are available.
Furthermore, EPA has concluded that, given the distribution of atrazine
use nationwide, the majority of water utilities will not be negatively
affected by the confirmation requirement and can take advantage of the
potential cost savings afforded by Method AG-625 relative to other
approved methods for atrazine. EPA notes that if utilities are
monitoring for a broad range of contaminants using approved methods
that cover multiple analytes (e.g., Method 525.2), then the use of a
test kit may not offer a cost advantage because of the ability to
include atrazine in a broad spectrum method.
Based on the data provided in response to the proposed rule and
NODA, EPA agrees that the presence of chlorine dioxide has substantial
potential to interfere with Method AG-625. Therefore, EPA has not
approved the method for use in water systems where chlorine dioxide is
used for drinking water treatment. While the data from one study
suggest that the atrazine results are not affected if samples are
analyzed within 24 hours after sample collection, the circumstances
surrounding this observation in the study have not been fully
characterized. At a future date, EPA may reconsider the use of Method
AG-625 by water systems using chlorine dioxide, if more information is
available characterizing the performance of the method.
B. Results From Use of Revised Methods, ``The Determination of Radium-
226 and Radium-228 in Drinking Water by Gamma-ray Spectrometry Using
HPGE or Ge(Li) Detectors.'' (Revision 1.2, December 2004)
The final rule establishing radionuclide drinking water standards
published on December 7, 2000 (65 FR 76708) required drinking water
systems to sample and report on radionuclides in their drinking water
supplies during the period from December 8, 2003 to December 31, 2007,
including the combined result for radium-226 and radium-228. Prior to
today's rule, separate methods were required for the measurement of
radium-226 and radium-228. The separate results of the two isotopes are
summed to provide the ``combined'' result that is compared to the MCL.
One commenter supported the approval of the method from the Georgia
Institute of Technology because one method can be used to measure both
radium isotopes and would make for a faster result. The commenter also
noted that there are approximately 150,000 Public Water Supply source
water taps across the country that would have to be sampled. Given
these monitoring requirements, the commenter was concerned about
sufficient laboratory capacity to meet the monitoring requirements of
the December 2000 rule because approval of the Georgia Institute of
Technology method would not become effective until promulgation of
today's rule.
In response to this comment, EPA is allowing community water
systems to use samples collected after January 1, 2005 and analyzed
using the analytical method approved in this rule to satisfy the
radium-226 and radium-228 monitoring requirements for the 2005-2007
compliance period. (Minor corrections to the method were made in
December 2004 and are reflected in the version approved in this rule,
so it was not available for analyzing samples collected prior to 2005.)
Allowing this early use of the method should alleviate some of the
laboratory capacity concerns. EPA has included a footnote in the
revised table of analytical methods for radioactivity at Sec. 141.25
to indicate that samples analyzed using the newly approved method are
acceptable. Such ``grandfathered'' data must be based on results from
the analytical method approved for use by this final rule. The term
``grandfathered data'' used in this rule does not apply to data
collected to meet other grandfathering provisions specified in the
radionuclide final rule that was published on December 7, 2000 (65 FR
76708).
V. Statutory and Executive Order Reviews
A. Executive Order 12866: Regulatory Planning and Review
Under Executive Order 12866 (58 FR 51735, October 4, 1993), the
Agency must determine whether the regulatory action is ``significant''
and therefore subject to OMB review and the requirements of the
Executive Order. The Executive Order defines ``significant regulatory
action'' as one that is likely to result in a rule that may:
(1) Have an annual effect on the economy of $100 million or more,
or adversely affect in a material way the economy, a sector of the
economy, productivity, competition, jobs, the environment, public
health or safety, or State, local, or Tribal governments or
communities;
(2) Create a serious inconsistency or otherwise interfere with an
action taken or planned by another agency;
(3) Materially alter the budgetary impact of entitlements, grants,
user fees, or loan programs or the rights and obligations of recipients
thereof; or
(4) Raise novel legal or policy issues arising out of legal
mandates, the President's priorities, or the principles set forth in
the Executive Order.
It has been determined that this rule is not a ``significant
regulatory action'' under the terms of Executive Order 12866 and is
therefore not subject to OMB review.
B. Paperwork Reduction Act
This action does not impose an information collection burden under
the provisions of the Paperwork Reduction