Expedited Approval of Alternative Test Procedures for the Analysis of Contaminants Under the Safe Drinking Water Act; Analysis and Sampling Procedures, 38348-38358 [E9-18361]
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Federal Register / Vol. 74, No. 147 / Monday, August 3, 2009 / Rules and Regulations
impact on a substantial number of small
entities under the Regulatory Flexibility
Act (5 U.S.C. 601 et seq.). Because this
rule approves pre-existing requirements
under State law and does not impose
any additional enforceable duty beyond
that required by State law, it does not
contain any unfunded mandate or
significantly or uniquely affect small
governments, as described in the
Unfunded Mandates Reform Act of 1995
(Pub. L. 104–4). This rule also does not
have Tribal implications because it will
not have a substantial direct effect on
one or more Indian Tribes, 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, as
specified by Executive Order 13175 (65
FR 67249, November 9, 2000). This
action also does not have Federalism
implications because it does 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 (64 FR 43255,
August 10, 1999). This action merely
approves a State rule implementing a
Federal requirement, and does not alter
the relationship or the distribution of
power and responsibilities established
in the CAA. This rule also is not subject
to Executive Order 13045 ‘‘Protection of
Children from Environmental Health
Risks and Safety Risks’’ (62 FR 19885,
April 23, 1997), because it approves a
State rule implementing a Federal
standard. In reviewing section 111(d)/
129 plan submissions, EPA’s role is to
approve State choices, provided that
they meet the criteria of the CAA. In this
context, in the absence of a prior
existing requirement for the State to use
voluntary consensus standards (VCS),
EPA has no authority to disapprove a
111(d)/129 plan submission for failure
to use VCS. It would thus be
inconsistent with applicable law for
EPA, when it reviews a 111(d)/129 plan
submission, to use VCS in place of a
111(d)/129 plan submission that
otherwise satisfies the provisions of the
CAA. Thus, the requirements of section
12(d) of the National Technology
Transfer and Advancement Act of 1995
(15 U.S.C. 272 note) do not apply. This
rule does not impose an information
collection burden under the provisions
of the Paperwork Reduction Act of 1995
(44 U.S.C. 3501 et seq.).
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B. Submission to Congress and the
Comptroller General
The Congressional Review Act, 5
U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement
Fairness Act of 1996, generally provides
that before a rule may take effect, the
agency promulgating the rule must
submit a rule report, which includes a
copy of the rule, to each House of the
Congress and to the Comptroller General
of the United States. EPA will submit a
report containing this rule and other
required information to the U.S. Senate,
the U.S. House of Representatives, and
the Comptroller General of the United
States prior to publication of the rule in
the Federal Register. This rule is not a
‘‘major rule’’ as defined by 5 U.S.C.
804(2).
C. Petitions for Judicial Review
Under section 307(b)(1) of the Clean
Air Act, petitions for judicial review of
this action must be filed in the United
States Court of Appeals for the
appropriate circuit by October 2, 2009.
Filing a petition for reconsideration by
the Administrator of this final rule does
not affect the finality of this rule for the
purposes of judicial review nor does it
extend the time within which a petition
for judicial review may be filed, and
shall not postpone the effectiveness of
such rule or action. Parties with
objections to this direct final rule are
encouraged to file a comment in
response to the parallel notice of
proposed rulemaking for this action
published in the proposed rules section
of today’s Federal Register, rather than
file an immediate petition for judicial
review of this direct final rule, so that
EPA can withdraw this direct final rule
and address the comment in the
proposed rulemaking. This action,
approving the submitted West Virginia
HMIWI plan revision, may not be
challenged later in proceedings to
enforce its requirements. (See section
307(b)(2).)
List of Subjects in 40 CFR Part 62
Environmental protection,
Administrative practice and procedure,
Air pollution control, Aluminum,
Fertilizers, Fluoride, Intergovernmental
relations, Paper and paper products
industry, Phosphate, Reporting and
recordkeeping requirements, Sulfur
oxides, Sulfur acid plants, Waste
treatment and disposal.
Dated: July 21, 2009.
William C. Early,
Acting Regional Administrator, Region III.
40 CFR Part 62, Subpart XX, is
amended as follows:
■
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PART 62—[AMENDED]
1. The authority citation for part 62
continues to read as follows:
■
Authority: 42 U.S.C. 7401 et seq.
Subpart XX—West Virginia
2. Section 62.12150 is amended by
designating the existing paragraph as
paragraph (a) and adding paragraph (b)
to read as follows:
■
§ 62.12150
Identification of plan.
*
*
*
*
*
(b) On May 11, 2009, the West
Virginia Department of Environmental
Protection submitted a State plan
revision (#1) that consolidates all
existing section 111(d)/129 incinerator
regulatory requirements into one
modified rule, WV45CSR18.
■ 3. Section 62.12152 is amended by
designating the existing paragraph as
paragraph (a) and adding paragraph (b)
to read as follows:
§ 61.12152
Effective date.
*
*
*
*
*
(b) Plan revision #1 is effective
October 2, 2009.
[FR Doc. E9–18482 Filed 7–31–09; 8:45 am]
BILLING CODE 6560–50–P
ENVIRONMENTAL PROTECTION
AGENCY
40 CFR Part 141
[EPA–HQ–OW–2009–0345; FRL–8930–8]
Expedited Approval of Alternative Test
Procedures for the Analysis of
Contaminants Under the Safe Drinking
Water Act; Analysis and Sampling
Procedures
AGENCY: Environmental Protection
Agency (EPA).
ACTION: Final rule.
SUMMARY: This action announces the
Environmental Protection Agency’s
(EPA’s) approval of alternative testing
methods for use in measuring the levels
of contaminants in drinking water and
determining compliance with national
primary drinking water regulations. The
Safe Drinking Water Act (SDWA)
authorizes EPA to approve the use of
alternative testing methods through
publication in the Federal Register. EPA
is using this streamlined authority to
make six additional methods available
for analyzing drinking water samples
required by regulation. This expedited
approach provides public water
systems, laboratories, and primacy
agencies with more timely access to new
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measurement techniques and greater
flexibility in the selection of analytical
methods, thereby reducing monitoring
costs while maintaining public health
protection.
DATES: This action is effective August 3,
2009.
FOR FURTHER INFORMATION CONTACT: Safe
Drinking Water Hotline (800) 426–4791
or Patricia Snyder Fair, Technical
Support Center, Office of Ground Water
and Drinking Water (MS 140),
Environmental Protection Agency, 26
West Martin Luther King Drive,
Cincinnati, OH 45268; telephone
number: (513) 569–7937; e-mail address:
fair.pat@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
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 SDWA may also measure
contaminants in water samples. When
EPA sets a monitoring requirement in its
national primary drinking water
regulations for a given contaminant, the
Agency also establishes in the
regulations standardized test procedures
for analysis of the contaminant. This
action makes alternative testing
methods available for particular
drinking water contaminants beyond the
testing methods currently established in
the regulations. EPA is providing public
water systems required to test water
samples with a choice of using either a
test procedure already established in the
existing regulations or an alternative test
procedure that has been approved in
this action. Categories and entities that
may ultimately be affected by this action
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 exhaustive, but rather
provides a guide for readers regarding
entities likely to be affected by this
action. This table lists the types of
entities that EPA is now aware could
potentially be affected by this action.
Other types of entities not listed in the
table could also be impacted. To
determine whether your facility is
affected 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 person listed in the preceding FOR
FURTHER INFORMATION CONTACT section.
B. How Can I Get Copies of This
Document and Other Related
Information?
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38349
1. Docket. EPA established a docket
for this action under Docket ID No.
EPA–HQ–OW–2009–0345. Publicly
available docket materials are available
either electronically through
www.regulations.gov or in hard copy at
the Water Docket in the EPA Docket
Center, (EPA/DC) EPA West, Room
3334, 1301 Constitution Ave., NW.,
Washington, DC. Copyrighted materials
are available only in hard copy. The
EPA Docket Center 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)
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566–1744, and the telephone number for
the Water Docket is (202) 566–2426.
2. Electronic Access. You may access
this Federal Register document
electronically through the EPA Internet
under the ‘‘Federal Register’’ listings at
https://www.epa.gov/fedrgstr/.
Abbreviations and Acronyms Used in
This Action
CFR: Code of Federal Regulations
DBCP: Dibromochloropropane
EDB: Ethylene Dibromide
EPA: Environmental Protection Agency
GC: Gas Chromatography
LED: Light-Emitting Diode
MS: Mass Spectrometry
NEMI: National Environmental Methods
Index
nm: Nanometers
SDWA: Safe Drinking Water Act
Table of Contents
I. General Information
A. Does This Action Apply to Me?
B. How Can I Get Copies of This Document
and Other Related Information?
II. Background
A. What Is the Purpose of This Action?
B. What Is the Basis for This Action?
III. Summary of Approvals
A. Methods Developed by EPA
B. Methods Developed by Vendors
IV. Statutory and Executive Order Reviews
V. References
II. Background
A. What Is the Purpose of This Action?
In this action, EPA is approving six
analytical methods for determining
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contaminant concentrations in samples
collected under SDWA. Regulated
parties required to sample and monitor
may use either the testing methods
already established in existing
regulations or the alternative testing
methods being approved in this action.
The new methods are listed in
Appendix A to Subpart C in 40 CFR 141
and on EPA’s drinking water methods
Web site at https://www.epa.gov/
safewater/methods/
analyticalmethods_expedited.html.
B. What Is the Basis for This Action?
When EPA determines an alternative
analytical method is ‘‘equally effective’’
(i.e., as effective as a method that has
already been promulgated in the
regulations), SDWA allows EPA to
approve the use of the alternative
method through publication in the
Federal Register. See Section 1401(1) of
SDWA. EPA is using this streamlined
approval authority to make six
additional methods available for
determining contaminant
concentrations in samples collected
under SDWA. EPA has determined that,
for each contaminant or group of
contaminants listed in Section III, the
additional testing methods being
approved in this action are equally as
effective as one or more of the testing
methods already established in the
regulations for those contaminants.
Section 1401(1) states that the newly
approved methods ‘‘shall be treated as
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an alternative for public water systems
to the quality control and testing
procedures listed in the regulation.’’
Accordingly, this action makes these
additional (and optional) six analytical
methods legally available for meeting
EPA’s monitoring requirements.
This action does not add regulatory
language, but does, for informational
purposes, update an appendix to the
regulations at 40 CFR part 141 that lists
all methods approved under Section
1401(1) of SDWA. Accordingly, while
this action is not a rule, it is updating
CFR text and therefore is being
published in the ‘‘Final Rules’’ section
of this Federal Register.
EPA described this expedited
methods approval process in an April
10, 2007, Federal Register notice (72 FR
17902) (USEPA 2007) and announced
its intent to begin using the process.
EPA published the first set of approvals
in a June 3, 2008, Federal Register
notice (73 FR 31616) (USEPA 2008) and
added Appendix A to 40 CFR Part 141,
Subpart C. This action adds six
additional methods to Appendix A to
Subpart C.
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III. Summary of Approvals
EPA is approving six methods that are
equally effective relative to methods
previously promulgated in the
regulations. By means of this notice,
these six methods are added to
Appendix A of 40 CFR Part 141, Subpart
C. For convenience of the reader, the
revised Appendix A in its entirety is
shown below. However, the only change
made to Appendix A through this action
is the inclusion of these six additional
methods as described in this preamble.
A. Methods Developed by EPA
EPA Method 524.3, Version 1.0. This
is a gas chromatography/mass
spectrometry (GC/MS) method for the
determination of purgeable organic
compounds in finished drinking waters.
The method analytes are purged from
the water sample using helium and
trapped on a sorbent material. After
purging, the trap is heated and back
flushed with helium to transfer the
analytes to a capillary GC column.
Compounds eluting from the GC are
directed into a mass spectrometer for
mass analysis and detection. The
analytes are identified by comparing the
acquired mass spectra and retention
times to reference spectra and retention
times for calibration standards acquired
under identical GC/MS conditions. The
concentration of each target analyte is
calculated using the internal standard
technique and response curves obtained
via procedural calibration. The
expansion of the method to include the
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option of selective ion monitoring
makes this method sufficiently sensitive
to measure dibromochloropropane
(DBCP) and ethylene dibromide (EDB) at
the concentrations required for drinking
water compliance monitoring.
EPA Method 524.3 is an updated
version of EPA Method 524.2, Revision
4.1 (USEPA 1995a), which is currently
approved for analyses of compliance
samples for 21 volatile organic
contaminants and total trihalomethanes.
The method development work is
described in the method research
summary (Zaffiro et al. 2009). The
advantages of the new method include:
• Use of maleic acid, a common food
preservative, to preserve samples,
eliminating the requirement to ship a
hazardous reagent (hydrochloric acid) to
the field;
• Incorporation of features that allow
users to take advantage of modern
instrumentation to improve speed and
data quality;
• Increased flexibility in selection of
method operating parameters; and
• Addition of Method 524.3 as an
approved method for DBCP and EDB.
Approved methods for volatile
organic contaminants and total
trihalomethanes are listed at 40 CFR
141.24(e). EPA Methods 502.2; Revision
2.1 (USEPA 1995b) and 524.2; Revision
4.1 (USEPA 1995a) are approved for
benzene; carbon tetrachloride;
chlorobenzene; 1,2-dichlorobenzene;
1,4-dichlorobenzene; 1,2dichloroethane; cis-dichloroethylene;
trans-dichloroethylene;
dichloromethane; 1,2-dichloropropane;
ethylbenzene; styrene;
tetrachloroethylene; 1,1,1trichloroethane; trichloroethylene;
toluene; 1,2,4-trichlorobenzene; 1,1dichloroethylene; 1,1,2-trichlorethane;
vinyl chloride; xylenes (total—measured
as sum of o-xylene; m-xylene and pxylene); and total trihalomethanes (sum
of chloroform; bromodichloromethane;
dibromochloromethane; and
bromoform). EPA Method 551.1 (USEPA
1995c) is approved for carbon
tetrachloride; tetrachloroethylene; 1,1,1trichloroethane; trichloroethylene; EDB;
DBCP; and total trihalomethanes. EPA
Method 504.1, Revision 1.1 (USEPA
1995d) is approved for EDB and DBCP.
Approved methods for total
trihalomethanes are also listed at 40
CFR 141.131(b)(1). For each of the 24
contaminants, the performance
characteristics of EPA Method 524.3
were compared to the characteristics of
each of the methods currently listed in
the regulations as approved for that
contaminant (Munch 2009). EPA has
determined that, for each of the 24
contaminants, EPA Method 524.3 is
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equally as effective for measuring the
contaminant as the methods currently
listed in the regulations as approved for
that contaminant. The basis for this
determination is discussed in Munch
2009. EPA is therefore approving use of
Method 524.3 for the above named 24
contaminants when analyzing drinking
water compliance samples.
EPA Method 524.3 Version 1.0
(USEPA 2009) can be accessed and
downloaded directly on-line at https://
epa.gov/safewater/methods/
analyticalmethods_ogwdw.html.
B. Methods Developed by Vendors
1. Mitchell Method M5271. Mitchell
Method M5271 (Mitchell 2009a) uses
laser nephelometry to measure turbidity
in drinking water. The method is based
on a comparison of the intensity of light
scattered by the sample under defined
conditions with the intensity of light
scattered by a standard reference
suspension. Readings are made using an
on-line laser nephelometer with the
following design criteria:
• Laser light source is monochromatic
operated at a nominal wavelength of 650
± 30nm;
• Incident radiation and any
convergence does not exceed ± 1.5
degrees in the measurement area;
• Distance traversed by incident light
and scattered light does not exceed
10cm;
• Detector/light receiver is centered at
90 ± 1.5 degrees to the incident light
path and the light cone does not exceed
± 30 degrees from 90 degrees; and
• Instrument incorporates a bubble
trap and anti-fog windows. Sensor is
horizontal and the windows are vertical.
Windows are immersed in the sample
stream.
Four approved methods for turbidity
are listed at 40 CFR 141.74(a)(1). The
performance characteristics of Mitchell
Method M5271 were compared to the
performance characteristics of approved
EPA Method 180.1 (USEPA 1993a). The
validation study report (Mitchell 2008a)
summarizes the results obtained from
the turbidimeters placed in series at
three different public water systems.
One water system used ground water
and the other two plants used surface
water sources. Measurements included
at least one filter backwash at each of
the surface water plants.
EPA has determined that the Mitchell
Method M5271 is equally effective
relative to EPA Method 180.1 that is
already promulgated in the regulations
at 40 CFR 141.74(a)(1). The basis for this
determination is discussed in
Wendelken 2009a. Therefore, EPA is
approving the Mitchell Method M5271
for determining turbidity in drinking
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water. A copy of the method can be
downloaded from the National
Environmental Methods Index (NEMI)
at https://www.nemi.gov or obtained by
contacting Leck Mitchell, PhD, PE, 656
Independence Valley Dr., Grand
Junction, CO 81507.
2. Mitchell Method M5331. Mitchell
Method M5331 (Mitchell 2009b) uses
light-emitting diode (LED)
nephelometry to measure turbidity in
drinking water. The method is based on
a comparison of the intensity of light
scattered by the sample under defined
conditions with the intensity of light
scattered by a standard reference
suspension. Readings are made using an
on-line LED nephelometer with the
following design criteria:
• LED light source is monochromatic
operated at a nominal wavelength of 525
± 15nm;
• Incident radiation and any
convergence does not exceed ± 1.5
degrees in the measurement area;
• Distance traversed by incident light
and scattered light does not exceed
10cm;
• Detector/light receiver is centered at
90 ± 1.5 degrees to the incident light
path and the light cone does not exceed
± 30 degrees from 90 degrees; and
• Instrument incorporates a bubble
trap and anti-fog windows. Sensor is
horizontal and the windows are vertical.
Windows are immersed in the sample
stream.
Four approved methods for turbidity
are listed at 40 CFR 141.74(a)(1). The
performance characteristics of Mitchell
Method M5331 were compared to the
performance characteristics of approved
EPA Method 180.1 (USEPA 1993a). The
validation study report (Mitchell 2008b)
summarizes the results obtained from
the turbidimeters placed in series at
three different public water systems.
One water system used ground water
and the other two plants used surface
water sources. Measurements included
at least one filter backwash at each of
the surface water plants.
EPA has determined that the Mitchell
Method M5331 is equally effective
relative to EPA Method 180.1 that is
already promulgated in the regulations
at 40 CFR 141.74(a)(1). The basis for this
determination is discussed in
Wendelken 2009b. Therefore, EPA is
approving it for determining turbidity in
drinking water. A copy of the method
can be downloaded from NEMI at
https://www.nemi.gov or obtained from
Leck Mitchell, PhD, PE, 656
Independence Valley Dr., Grand
Junction, CO 81507.
3. Orion Method AQ4500. Thermo
Scientific’s Orion Method AQ4500
(Thermo Scientific 2009) uses LED
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nephelometry to measure turbidity in
drinking water. The method is based on
a comparison of the intensity of light
scattered by the sample at 90 degrees to
the beam path with the intensity of light
scattered by a standard reference
suspension. Readings are made using a
portable LED nephelometer with the
following design criteria:
• White LED light source emits
broadband light having peak intensities
in the 400nm to 600nm range;
• Distance traversed by incident light
and scattered light does not exceed
10cm;
• Detector/light receiver is centered at
90 degrees to the incident light path and
the light cone does not exceed ± 30
degrees from 90 degrees. The detector
has spectral peak response between
400nm and 600nm;
• Pulsed light allows for synchronous
detection, a technique by which
ambient stray light leakage, as well as
other electronic induced errors, are
effectively cancelled out; and
• Color compensation is achieved
using a dual-beam system with two
photo detectors.
Four approved methods for turbidity
are listed at 40 CFR 141.74(a)(1). The
performance characteristics of Thermo
Scientific’s Orion Method AQ4500 were
compared to the performance
characteristics of EPA Method 180.1
(USEPA 1993a) listed at 40 CFR
141.74(a)(1) for measurement of
turbidity. Two rounds of testing were
conducted (Wendelken 2009c). The first
was an ASTM round robin study
comparing results from analyses of 28
samples of various types using
turbidimeters with tungsten filament
light sources as specified in EPA
Method 180.1 and white LEDs as
specified in Thermo Scientific Orion
Method AQ4500. A second study
involved demonstration of performance
at turbidities below 2 nephelometric
turbidity units.
EPA has determined that Thermo
Scientific’s Orion Method AQ4500 is
equally effective relative to EPA Method
180.1, which is already promulgated in
the regulations at 40 CFR 141.74(a)(1).
The basis for this determination is
discussed in Wendelken 2009c.
Therefore, EPA is approving Method
AQ4500 for the measurement of
turbidity in drinking water. A copy of
the method can be downloaded from
NEMI at https://www.nemi.gov or
obtained from Thermo Scientific, 166
Cummings Center, Beverly, MA 01915,
Phone: (800) 225–1480,
www.thermo.com.
4. Systea Easy (1-Reagent). Systea
Scientific, LLC’s Systea Easy (1-Reagent)
Nitrate Method uses automated discreet
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analysis by spectrophotometry to
determine concentrations of nitrate and
nitrite combined or individually in
drinking water. The method involves
the following steps:
• Reduction of nitrate in a sample to
nitrite using a non-hazardous
proprietary reagent;
• Diazotizing the nitrite originally in
the sample plus the reduced nitrate with
sulfanilamide followed by coupling
with N-(1-napthyl)ethylenediamine
dihydrochloride under acidic
conditions to form a highly colored azo
dye;
• Colorimetric determination in
which the absorbance of color at 546nm
is directly proportional to the
concentration of the nitrite plus the
reduced nitrate in the sample;
• Measurement of nitrite individually
by analysis of the sample while
eliminating the reduction step; and
• Subtraction of the nitrite value from
that of the combined nitrate plus nitrite
value to determine nitrate individually.
Approved methods for nitrate and
nitrite are listed at 40 CFR 141.23(k)(1).
An inter-laboratory study (Systea
Scientific, LLC. 2008) was conducted to
compare the performance characteristics
of the Systea Easy (1-Reagent) Nitrate
Method to the characteristics of the EPA
Method 353.2 (USEPA 1993b) and
Standard Method 4500–NO3¥ F–00
(APHA 1997), which are listed at 40
CFR 141.23(k)(1) for nitrate and nitrite.
Ten laboratories analyzed a variety of
sample matrices using approved
methods. The samples were also
analyzed using the Systea Easy (1Reagent) Nitrate Method.
EPA has determined that the Systea
Easy (1-Reagent) Nitrate Method is
equally effective relative to EPA Method
353.2 and Standard Method 4500–NO3¥
F–00, which are already promulgated in
the regulations. The basis for this
determination is discussed in
Wendelken 2009d. The method is a
‘‘green’’ alternative to other approved
methods, which use cadmium, a known
carcinogen, for the reduction of nitrate
to nitrite. EPA is approving this method
for determining nitrate and nitrite
concentrations in drinking water to
comply with 40 CFR 141.23.
Systea Easy (1-Reagent) Nitrate
Method (Systea Scientific, LLC. 2009)
can be downloaded from NEMI at
https://www.nemi.gov or obtained from
Systea Scientific, LLC, 900 Jorie Blvd.,
Suite 35, Oak Brook, IL 60523, Phone:
(630) 645–0600.
5. Method ME355.01. ‘‘Determination
of Cyanide in Drinking Water by GC/MS
Headspace’’ (Eaton 2009) uses direct
headspace injection after acidification
followed by Gas Chromatography/Mass
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Spectrometry (GC/MS) to determine the
concentration of cyanide, as free
cyanide, in drinking water. The method
involves the following steps:
• Acidification of the sample;
• Heating the sample to 60 degrees
Celsius with agitation;
• Direct injection of 1 milliliter of
headspace onto the nitrogen cooled
cryotrap; and
• Analysis using temperature
programmed GC/MS.
The performance characteristics of
Method ME355.01 were determined in
three laboratories by replicate analyses
of fortified samples (Wendelken 2009e).
The results were compared to the
characteristics of EPA Method 335.4
(USEPA 1993c) and Standard Method
4500–CN¥ F–99 (APHA 1999) listed at
40 CFR 141.23(k)(1) for cyanide. EPA
has determined that Method ME355.01
is equally effective relative to each of
these two methods. The basis for this
determination is discussed in
Wendelken 2009e. Therefore, EPA is
approving this method for determining
cyanide concentrations in drinking
water to comply with 40 CFR 141.23.
Method ME335.01 can be downloaded
from NEMI at https://www.nemi.gov or
obtained from James Eaton, PhD, H & E
Testing Laboratory, 221 State Street,
Augusta, ME 04333, Phone: (207) 187–
2727.
sroberts on DSKD5P82C1PROD with RULES
IV. Statutory and Executive Order
Reviews
As noted above, under the terms of
SDWA Section 1401(1), this streamlined
method approval action is not a rule.
Accordingly, the Congressional Review
Act, 5 U.S.C. 801 et seq., as added by
the Small Business Regulatory
Enforcement Fairness Act of 1996, does
not apply because this action is not a
rule for purposes of 5 U.S.C. 804(3).
Similarly, this action is not subject to
the Regulatory Flexibility Act because it
is not subject to notice and comment
requirements under the Administrative
Procedure Act or any other statute. In
addition, because this approval action is
not a rule but simply makes alternative
(optional) testing methods available for
monitoring under SDWA, EPA has
concluded that other statutes and
executive orders generally applicable to
rulemaking do not apply to this
approval action.
V. References
American Public Health Association
(APHA), 2000. Standard Method 4500–
NO3¥ F–00. Automated Cadmium
Reduction Method. Approved by
Standard Methods Committee 2000.
Standard Methods Online. (Available at
https://www.standardmethods.org.)
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15:47 Jul 31, 2009
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American Public Health Association
(APHA), 1999. Standard Method 4500–
CN¥ F–99. Cyanide-Selective Electrode
Method. Approved by Standard
Methods Committee 1999. Standard
Methods Online. (Available at https://
www.standardmethods.org.)
Eaton, J. 2009. Method ME355.01,
Revision 1.0. Determination of Cyanide
in Drinking Water by GC/MS
Headspace. May 26, 2009. H & E Testing
Laboratory, 221 State Street, Augusta,
ME 04333. (Available at https://
www.nemi.gov.)
Mitchell, L. and Mitchell, P., 2008a.
Mitchell ATP Submission for Changes
in Method 180.1 Using Laser
Determination of Turbidity by
Nephelometry, Mitchell Method M5271,
Validation Study Report, Revision 1.0,
July 31, 2008. 656 Independence Valley
Dr., Grand Junction, CO 81507.
Mitchell, L. and Mitchell, P., 2008b.
Mitchell ATP Submission for Changes
in Method 180.1 Using LED
Determination of Turbidity by
Nephelometry, Mitchell Method M5331,
Validation Study Report, Revision 1.0,
July 31, 2008. 656 Independence Valley
Dr., Grand Junction, CO 81507.
Mitchell, L. and Mitchell, P., 2009a.
Mitchell Method M5271, Revision 1.1.
Determination of Turbidity by Laser
Nephelometry, March 5, 2009. Leck
Mitchell, PhD, PE, 656 Independence
Valley Dr., Grand Junction, CO 81507.
(Available at https://www.nemi.gov.)
Mitchell, L. and Mitchell, P., 2009b.
Mitchell Method M5331, Revision 1.1.
Determination of Turbidity by LED
Nephelometry, March 5, 2009. Leck
Mitchell, PhD, PE, 656 Independence
Valley Dr., Grand Junction, CO 81507.
(Available at https://www.nemi.gov.)
Munch, D., 2009. Memo to the record
describing basis for expedited approval
of EPA Method 524.3. May 22, 2009.
Systea Scientific, LLC., 2008.
Validation Study Report for New
Method Approval of Nitrate Analysis in
Wastewater and Drinking Water
Utilizing Systea Scientific, LLC NonHazardous Proprietary Reagent R1,
Systea Easy (1-Reagent) Nitrate 0.050–10
mg/L. September 15, 2008. 900 Jorie
Blvd., Suite 35, Oak Brook, IL 60523.
Systea Scientific, LLC., 2009. Systea
Easy (1-Reagent) Nitrate Method,
February 4, 2009. 900 Jorie Blvd., Suite
35, Oak Brook, IL 60523. (Available at
https://www.nemi.gov.)
Thermo Scientific, 2009. Orion
Method AQ4500, Revision 1.0.
Determination of Turbidity by LED
Nephelometry, May 8, 2009. 166
Cummings Center, Beverly, MA 01915.
(Available at https://www.nemi.gov.)
USEPA. 1993a. EPA Method 180.1,
Revision 2.0, ‘‘Determination of
PO 00000
Frm 00030
Fmt 4700
Sfmt 4700
Turbidity by Nephelometry’’ in Methods
for the Determination of Inorganic
Substances in Environmental Samples,
EPA/600/R–93/100. (Available at
https://www.nemi.gov.)
USEPA. 1993b. EPA Method 353.2,
Revision 2.0, ‘‘Determination of NitrateNitrite Nitrogen by Automated
Colorimetry’’ in Methods for the
Determination of Inorganic Substances
in Environmental Samples, EPA/600/R–
93/100. (Available at https://
www.nemi.gov.)
USEPA. 1993c. EPA Method 335.4,
Revision 1.0, ‘‘Determination of Total
Cyanide by Semi-Automated
Colorimetry’’ in Methods for the
Determination of Inorganic Substances
in Environmental Samples, EPA/600/R–
93/100. (Available at https://
www.nemi.gov.)
USEPA. 1995a. EPA Method 524.2,
Revision 4.1, ‘‘Measurement of
Purgeable Organic Compounds in Water
by Capillary Column Gas
Chromatography/Mass Spectrometry’’ in
Methods for the Determination of
Organic Compounds in Drinking
Water—Supplement III, EPA/600/R–95–
131. (Available at https://www.nemi.gov.)
USEPA. 1995b. EPA Method 502.2,
Revision 2.1, ‘‘Volatile Organic
Compounds in Water by Purge and Trap
Capillary Column Gas Chromatography
with Photoionization and Electrolytic
Conductivity Detectors in Series’’ in
Methods for the Determination of
Organic Compounds in Drinking
Water—Supplement III, EPA/600/R–95–
131. (Available at https://www.nemi.gov.)
USEPA. 1995c. EPA Method 551.1,
Revision 1.0, ‘‘Determination of
Chlorination Disinfection Byproducts,
Chlorinated Solvents, and Halogenated
Pesticides/Herbicides in Drinking Water
by Liquid-Liquid Extraction and Gas
Chromatography with Electron-Capture
Detection’’ in Methods for the
Determination of Organic Compounds
in Drinking Water—Supplement III,
EPA/600/R–95–131. (Available at
https://www.nemi.gov.)
USEPA. 1995d. EPA Method 504.1,
Revision 1.1, ‘‘1,2-Dibromoethane
(EDB), 1,2-Dibromo-3-Chloro-Propane
(DBCP), and 1,2,3-Trichloropropane
(123TCP) in Water by Microextraction
and Gas Chromatography’’ in Methods
for the Determination of Organic
Compounds in Drinking Water—
Supplement III, EPA/600/R–95–131.
(Available at https://www.nemi.gov.)
USEPA. 2007. Expedited Approval of
Test Procedures for the Analysis of
Contaminants Under the Safe Drinking
Water Act; Analysis and Sampling
Procedures. 72 FR 17902. April 10,
2007.
E:\FR\FM\03AUR1.SGM
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Federal Register / Vol. 74, No. 147 / Monday, August 3, 2009 / Rules and Regulations
USEPA. 2008. Expedited Approval of
Alternative Test Procedures for the
Analysis of Contaminants Under the
Safe Drinking Water Act; Analysis and
Sampling Procedures. 73 FR 31616. June
3, 2008.
USEPA. 2009. EPA Method 524.3
Version 1.0. Measurement of Purgeable
Organic Compounds in Water by
Capillary Column Gas Chromatography/
Mass Spectrometry, EPA 815–B–09–009.
June 2009. (Available at https://epa.gov/
safewater/methods/
analyticalmethods_ogwdw.html.)
Wendelken, S., 2009a. Memo to the
record describing basis for expedited
approval of Mitchell Method M5271.
May 29, 2009.
Wendelken, S., 2009b. Memo to the
record describing basis for expedited
approval of Mitchell Method M5331.
May 29, 2009.
Wendelken, S., 2009c. Memo to the
record describing ATP evaluation of
38353
Thermo Scientific/Orion Method
AQ4500, Revision 1.0 and basis for
expedited approval. May 29, 2009.
Wendelken, S., 2009d. Memo to the
record describing basis for expedited
approval of Systea Easy (1–Reagent)
Nitrate Method. May 29, 2009.
Wendelken, S., 2009e. Memo to the
record describing ATP evaluation of
Method ME355.01 and basis for
expedited approval. May 29, 2009.
Zaffiro, A.D, Prakash, B. and
Zimmerman, M., 2009. EPA Method
524.3 Research Summary, Shaw
Environmental, Cincinnati OH. June
2009.
Dated: July 9, 2009.
Michael H. Shapiro,
Acting Assistant Administrator, Office of
Water.
List of Subjects in 40 CFR Part 141
Appendix A to Subpart C of Part 141—
Alternative Testing Methods Approved
for Analyses Under the Safe Drinking
Water Act
For the reasons stated in the preamble,
40 CFR part 141 is amended as follows:
■
PART 141—NATIONAL PRIMARY
DRINKING WATER REGULATIONS
1. The authority citation for part 141
continues to read as follows:
■
Authority: 42 U.S.C. 300f, 300g–1, 300j–4,
and 300j–9.
2. Subpart C is amended by revising
Appendix A to read as follows:
■
Environmental protection, Chemicals,
Indians—lands, Intergovernmental
relations, Radiation protection,
Reporting and recordkeeping
requirements, Water supply.
Only the editions stated in the following
table are approved.
ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 141.21(f)(3)
SM 21st edition 1
Organism
Methodology
Total Coliforms ........................
Total Coliform Fermentation Technique ..................................................................................
Total Coliform Membrane Filter Technique .............................................................................
Presence-Absence (P–A) Coliform Test .................................................................................
ONPG–MUG Test ....................................................................................................................
9221 A, B
9222 A, B, C
9221 D
9223
ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 141.23(k)(1)
Contaminant
Methodology
Alkalinity ..........
Antimony .........
Titrimetric ..................................
Atomic Absorption; Furnace .....
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Atomic Absorption; Furnace .....
Hydride Atomic Absorption .......
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Inductively Coupled Plasma .....
Atomic Absorption; Direct .........
Atomic Absorption; Furnace .....
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Inductively Coupled Plasma .....
Atomic Absorption; Furnace .....
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Atomic Absorption; Furnace .....
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
EDTA titrimetric ........................
Atomic Absorption; Direct Aspiration.
Inductively Coupled Plasma .....
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Inductively Coupled Plasma .....
Atomic Absorption; Furnace .....
Arsenic ............
Barium .............
Beryllium ..........
Cadmium .........
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Calcium ...........
Chromium ........
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EPA method
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ASTM 4
2320 B
3113 B
200.5, Revision
4.2 2.
3113 B
3114 B
200.5, Revision
4.2.
3120 B
3111 D
3113 B
200.5, Revision
4.2.
3120 B
3113 B
200.5, Revision
4.2.
3113 B
200.5, Revision
4.2.
3500–Ca B
3111 B
3120 B
200.5, Revision
4.2.
3120 B
3113 B
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ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 141.23(k)(1)—Continued
Contaminant
Methodology
Copper .............
Conductivity .....
Cyanide ...........
Fluoride ...........
Lead ................
Magnesium ......
Mercury ...........
Nickel ...............
Nitrate ..............
Nitrite ...............
Orthophosphate
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pH ....................
Selenium .........
Silica ................
VerDate Nov<24>2008
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Atomic Absorption; Furnace .....
Atomic Absorption; Direct Aspiration.
Inductively Coupled Plasma .....
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Conductance .............................
Manual Distillation followed by
Spectrophotometric,
Amenable.
Spectrophotometric Manual ..
Selective Electrode ...................
Gas Chromatography/Mass
Spectrometry Headspace.
Ion Chromatography .................
Manual Distillation; Colorimetric
SPADNS.
Manual Electrode ......................
Automated Alizarin ...................
Atomic Absorption; Furnace .....
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Atomic Absorption ....................
Inductively Coupled Plasma .....
Complexation Titrimetric Methods.
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Manual, Cold Vapor ..................
Inductively Coupled Plasma .....
Atomic Absorption; Direct .........
Atomic Absorption; Furnace .....
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Ion Chromatography .................
Automated Cadmium Reduction
Manual Cadmium Reduction ....
Ion Selective Electrode .............
Reduction/Colorimetric .............
SM 21st
edition 1
EPA method
SM online 3
ASTM 4
Other
200.5, Revision
4.2.
3113 B
3111 B
3120 B
200.5, Revision
4.2.
2510 B
4500–CN¥ G
D2036–06 A
D2036–06 B
4500–CN¥ E
4500–CN¥ F
D2036–06 A
ME355.01 7
4110 B
4500–F¥ B, D
4500–F¥ C
4500–F¥ E
3113 B
D1179–04 B
200.5, Revision
4.2.
3111 B
3120 B
3500–Mg B
200.5, Revision
4.2.
3112
3120
3111
3113
B
B
B
B
200.5, Revision
4.2.
4110 B
4500–NO3¥ F
4500–NO3¥ E
4500–NO3¥ D
Systea Easy
(1-Reagent) 8
Ion Chromatography .................
Automated Cadmium Reduction
Manual Cadmium Reduction ....
Spectrophotometric ...................
Reduction/Colorimetric .............
4110 B
4500–NO3¥ F
4500–NO3¥ E
4500–NO2¥ B
Ion Chromatography .................
Colorimetric, ascorbic acid, single reagent.
Colorimetric, Automated, Ascorbic Acid.
Electrometric .............................
Hydride-Atomic Absorption .......
Atomic Absorption; Furnace .....
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Colorimetric ...............................
Molybdosilicate .........................
Heteropoly blue ........................
Automated for Molybdate-reactive Silica.
4110 B
4500–P E
4500–P E–99
4500–P F
4500–P F–99
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(1-Reagent) 8
4500–H+ B
3114 B
3113 B
200.5, Revision
4.2.
D859–05
4500–SiO2 C
4500–SiO2 D
4500–SiO2 E
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ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 141.23(k)(1)—Continued
Contaminant
Methodology
SM online 3
ASTM 4
200.5, Revision
4.2.
Sodium ............
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Inductively Coupled Plasma .....
Atomic Absorption; Direct Aspiration.
Axially viewed inductively coupled plasma-atomic emission
spectrometry (AVICP–AES).
Thermometric ............................
SM 21st
edition 1
EPA method
Temperature ....
Other
3120 B
3111 B
200.5, Revision
4.2.
2550
ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 141.24(e)(1)
Contaminant
Methodology
Benzene ..................................
Carbon tetrachloride ...............
Chlorobenzene ........................
1,2-Dichlorobenzene ...............
1,4-Dichlorobenzene ...............
1,2-Dichloroethane ..................
cis-Dichloroethylene ................
Trans-Dichloroethylene ...........
Dichloromethane .....................
1,2-Dichloropropane ...............
Ethylbenzene ..........................
Styrene ....................................
Tetrachloroethylene ................
1,1,1-Trichloroethane ..............
Trichloroethylene ....................
Toluene ...................................
1,2,4-Trichlorobenzene ...........
1,1-Dichloroethylene ...............
1,1,2-Trichlorethane ................
Vinyl chloride ..........................
Xylenes (total) .........................
Carbofuran ..............................
Dibromochloropropane
(DBCP).
Ethyl dibromide (EDB) ............
Oxamyl ....................................
Total Trihalomethanes ............
EPA method
........
........
........
........
........
........
........
........
........
........
........
........
........
........
........
........
........
........
........
........
........
post-
524.3
Purge & Trap/Gas Chromatography/Mass Spectrometry ........
High-performance liquid chromatography (HPLC) with postcolumn derivatization and fluorescence detection.
Purge & Trap/Gas Chromatography/Mass Spectrometry ........
SM online 3
524.3 9
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
524.3
........
SM 21st
edition 1
524.3
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
Purge & Trap/Gas Chromatography/Mass Spectrometry
High-performance liquid chromatography (HPLC) with
column derivatization and fluorescence detection.
Purge & Trap/Gas Chromatography/Mass Spectrometry
6610 B
6610 B–04
6610 B
6610 B–04
524.3
ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 141.25(a)
Contaminant
Naturally Occurring:
Gross alpha and beta ...........................................
Gross alpha ...........................................................
Radium 226 ...........................................................
Evaporation ..................................................................
Coprecipitation .............................................................
Radon emanation .........................................................
Radiochemical ..............................................................
Radiochemical ..............................................................
Radiochemical ..............................................................
ICP–MS ........................................................................
Alpha spectrometry ......................................................
Radioactive Iodine .................................................
Radiochemical ..............................................................
Gamma Ray Spectrometry ..........................................
Radiochemical ..............................................................
Radioactive Strontium 89, 90 ................................
Tritium ...................................................................
Gamma Ray Spectrometry ..........................................
Radiochemical ..............................................................
Liquid Scintillation ........................................................
7500–Cs B
7120
7500–I B
7500–I C
7500–I D
7120
7500–Sr B
7500–3H B
ASTM 4
7110 B
7110 C
7500–Ra C
7500–Ra B
7500–Ra D
7500–U B
Radium 228 ...........................................................
Uranium .................................................................
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SM 21st
edition 1
Methodology
Man-Made:
Radioactive Cesium ..............................................
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ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 141.25(a)—Continued
Contaminant
SM 21st
edition 1
Methodology
Gamma Emitters ...................................................
Gamma Ray Spectrometry ..........................................
ASTM 4
7120
7500–Cs B
7500–I B
ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 141.74(a)(1)
SM 21st
edition 1
Organism
Methodology
Total Coliform ..................
Total Coliform Fermentation Technique ............................................................
Total Coliform Membrane Filter Technique ......................................................
ONPG–MUG Test .............................................................................................
Fecal Coliform Procedure .................................................................................
Fecal Coliform Filter Procedure ........................................................................
Pour Plate Method ............................................................................................
Nephelometric Method ......................................................................................
Laser Nephelometry (on-line) ............................................................................
LED Nephelometry (on-line) ..............................................................................
LED Nephelometry (portable) ...........................................................................
Fecal Coliforms ...............
Heterotrophic bacteria .....
Turbidity ..........................
9221
9222
9223
9221
9222
9215
2130
Other
A, B, C
A, B, C
E
D
B
B
Mitchell M527110
Mitchell M5331 11
Orion AQ4500 12
ALTERNATIVE TESTING METHODS FOR DISINFECTANT RESIDUALS LISTED AT 40 CFR 141.74(a)(2)
SM 21st
edition 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 ................................................................................................................
Amperometric Titration ................................................................................................................
Indigo Method .............................................................................................................................
Total Chlorine ...........................
Chlorine Dioxide .......................
Ozone .......................................
4500–Cl D
4500–Cl F
4500–Cl G
4500–Cl H
4500–Cl D
4500–Cl E
4500–Cl F
4500–Cl G
4500–Cl I
4500–ClO2 C
4500–ClO2 E
4500–O3 B
ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 141.131(b)(1)
Contaminant
Methodology
EPA method
TTHM ..........................................................................
HAA5 ..........................................................................
Chlorite—daily monitoring as prescribed in 40 CFR
141.132(b)(2)(i)(A).
P&T/GC/MS ................................................................
LLE (diazomethane)/GC/ECD ....................................
Amperometric Titration ...............................................
SM 21st edition 1
524.3 9
6251 B
4500–ClO2 E
ALTERNATIVE TESTING METHODS FOR DISINFECTANT RESIDUALS LISTED AT 40 CFR 141.131(c)(1)
SM 21st edition 1
Residual
Methodology
Free Chlorine ..........................
Amperometric Titration ............................................................................................................
DPD Ferrous Titrimetric ...........................................................................................................
DPD Colorimetric .....................................................................................................................
Syringaldazine (FACTS) ..........................................................................................................
Amperometric Titration ............................................................................................................
DPD Ferrous Titrimetric ...........................................................................................................
DPD Colorimetric .....................................................................................................................
Amperometric Titration ............................................................................................................
Low level Amperometric Titration ............................................................................................
DPD Ferrous Titrimetric ...........................................................................................................
DPD Colorimetric .....................................................................................................................
Iodometric Electrode ................................................................................................................
Amperometric Method II ..........................................................................................................
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Combined Chlorine .................
Total Chlorine .........................
Chlorine Dioxide .....................
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4500–Cl D
4500–Cl F
4500–Cl G
4500–Cl H
4500–Cl D
4500–Cl F
4500–Cl G
4500–Cl D
4500–Cl E
4500–Cl F
4500–Cl G
4500–Cl I
4500–ClO2 E
38357
Federal Register / Vol. 74, No. 147 / Monday, August 3, 2009 / Rules and Regulations
ALTERNATIVE TESTING METHODS FOR DISINFECTANT RESIDUALS LISTED AT 40 CFR 141.131(c)(2), IF APPROVED BY THE
STATE
Residual
Methodology
Method
Free Chlorine ..........................
Test Strips ...............................................................................................................................
Method D99–003 5
ALTERNATIVE TESTING METHODS FOR PARAMETERS LISTED AT 40 CFR 141.131(d)
SM 21st edition 1
Parameter
Methodology
Total Organic Carbon (TOC) ..................
High Temperature Combustion ...............................................................................
Persulfate-Ultraviolet or Heated Persulfate Oxidation .............................................
Wet Oxidation ..........................................................................................................
Calculation using DOC and UV254 data ..................................................................
High Temperature Combustion ...............................................................................
Persulfate-Ultraviolet or Heated Persulfate Oxidation .............................................
Wet Oxidation ..........................................................................................................
Spectrophotometry ...................................................................................................
Specific Ultraviolet Absorbance (SUVA)
Dissolved Organic Carbon (DOC) ...
Ultraviolet absorption at 254 nm
(UV254).
5310 B
5310 C
5310 D
5310
5310
5310
5910
B
C
D
B
ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 141.402(c)(2)
SM 20th
edition 6
Organism
Methodology
E. coli .....................................
Colilert ....................................................................................
Colisure ..................................................................................
Colilert-18 ...............................................................................
Multiple-Tube Technique ........................................................
Enterococci ............................
SM 21st
edition 1
9223 B
9223 B
9223 B
9223 B
SM online 3
9223
9223
9223
9230
B–97
B–97
B–97
B–04
ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 141.704(b)
SM 20th edition 6
Organism
Methodology
E. coli ............................
Membrane Filtration, Two Step .........................................................................................................
9222 D/9222 G
ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 143.4(b)
Methodology
EPA method
Aluminum .........
Axially viewed inductively coupled plasma-atomic
emission spectrometry (AVICP–AES).
Atomic Absorption; Direct .....................................
Atomic Absorption; Furnace .................................
Inductively Coupled Plasma .................................
Silver Nitrate Titration ...........................................
Ion Chromatography .............................................
Potentiometric Titration .........................................
Visual Comparison ................................................
Methylene Blue Active Substances (MBAS) ........
Axially viewed inductively coupled plasma-atomic
emission spectrometry (AVICP–AES).
Atomic Absorption; Direct .....................................
Atomic Absorption; Furnace .................................
Inductively Coupled Plasma .................................
Axially viewed inductively coupled plasma-atomic
emission spectrometry (AVICP–AES).
Atomic Absorption; Direct .....................................
Atomic Absorption; Furnace .................................
Inductively Coupled Plasma .................................
Threshold Odor Test .............................................
Axially viewed inductively coupled plasma-atomic
emission spectrometry (AVICP–AES).
Atomic Absorption; Direct .....................................
Atomic Absorption; Furnace .................................
Inductively Coupled Plasma .................................
Ion Chromatography .............................................
Gravimetric with ignition of residue ......................
Gravimetric with drying of residue ........................
Turbidimetric method ............................................
SM 21st
edition 1
3111 D
3113 B
3120 B
4500–Cl¥ B
4110 B
4500–Cl¥ D
2120 B
5540 C
SM online 3
200.5, Revision
4.2 2.
Chloride ............
Color .................
Foaming Agents
Iron ...................
Manganese ......
Odor .................
Silver ................
sroberts on DSKD5P82C1PROD with RULES
ASTM 4
D 512–04 B
Contaminant
Sulfate ..............
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4.2.
3111 B
3113 B
3120 B
200.5, Revision
4.2.
3111
3113
3120
2150
B
B
B
B
200.5, Revision
4.2.
Fmt 4700
3111 B
3113 B
3120 B
4110 B
4500–SO4¥2 C
4500–SO4¥2 D
4500–SO4¥2 E
Sfmt 4700
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4500–SO4¥2 C–97
4500–SO4¥2 D–97
4500–SO4¥2 E–97
38358
Federal Register / Vol. 74, No. 147 / Monday, August 3, 2009 / Rules and Regulations
ALTERNATIVE TESTING METHODS FOR CONTAMINANTS LISTED AT 40 CFR 143.4(b)—Continued
Contaminant
Methodology
sroberts on DSKD5P82C1PROD with RULES
Total Dissolved
Solids.
Zinc ..................
ASTM 4
Axially viewed inductively coupled plasma-atomic
emission spectrometry (AVICP–AES).
Atomic Absorption; Direct Aspiration ....................
Inductively Coupled Plasma .................................
15:47 Jul 31, 2009
Jkt 217001
4500–SO4¥2 F–97
3111 B
3120 B
BILLING CODE S
DEPARTMENT OF HOMELAND
SECURITY
Federal Emergency Management
Agency
44 CFR Part 64
[Docket ID FEMA–2008–0020; Internal
Agency Docket No. FEMA–8085]
Suspension of Community Eligibility
AGENCY: Federal Emergency
Management Agency, DHS.
ACTION: Final rule.
SUMMARY: This rule identifies
communities, where the sale of flood
insurance has been authorized under
the National Flood Insurance Program
(NFIP), that are scheduled for
suspension on the effective dates listed
within this rule because of
noncompliance with the floodplain
management requirements of the
program. If the Federal Emergency
Management Agency (FEMA) receives
documentation that the community has
adopted the required floodplain
management measures prior to the
effective suspension date given in this
rule, the suspension will not occur and
a notice of this will be provided by
publication in the Federal Register on a
subsequent date.
DATES: Effective Dates: The effective
date of each community’s scheduled
suspension is the third date (‘‘Susp.’’)
listed in the third column of the
following tables.
FOR FURTHER INFORMATION CONTACT: If
you want to determine whether a
particular community was suspended
Frm 00036
SM online 3
200.5, Revision
4.2.
https://www.nemi.gov or from Leck Mitchell,
PhD, PE, 656 Independence Valley Dr., Grand
Junction, CO 81507.
12 Orion Method AQ4500, Revision 1.0.
‘‘Determination of Turbidity by LED
Nephelometry,’’ May 8, 2009. Available at
https://www.nemi.gov or from Thermo
Scientific, 166 Cummings Center, Beverly,
MA 01915, https://www.thermo.com.
[FR Doc. E9–18361 Filed 7–31–09; 8:45 am]
PO 00000
SM 21st
edition 1
4500–SO4¥2 F
2540 C
Automated methylthymol blue method .................
Total Dissolved Solids Dried at 180 deg C ..........
1 Standard Methods for the Examination of
Water and Wastewater, 21st edition (2005).
Available from American Public Health
Association, 800 I Street, NW., Washington,
DC 20001–3710.
2 EPA Method 200.5, Revision 4.2.
‘‘Determination of Trace Elements in
Drinking Water by Axially Viewed
Inductively Coupled Plasma-Atomic
Emission Spectrometry.’’ 2003. EPA/600/R–
06/115. (Available at https://www.epa.gov/
nerlcwww/ordmeth.htm.)
3 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.
4 Available from ASTM International, 100
Barr Harbor Drive, West Conshohocken, PA
19428–2959 or https://astm.org. The methods
listed are the only alternative versions that
may be used.
5 Method D99–003, Revision 3.0. ‘‘Free
Chlorine Species (HOCl¥ and OCl¥) by Test
Strip,’’ November 21, 2003. Available from
Industrial Test Systems, Inc., 1875 Langston
St., Rock Hill, SC 29730.
6 Standard Methods for the Examination of
Water and Wastewater, 20th edition (1998).
Available from American Public Health
Association, 800 I Street, NW., Washington,
DC 20001–3710.
7 Method ME355.01, Revision 1.0.
‘‘Determination of Cyanide in Drinking Water
by GC/MS Headspace,’’ May 26, 2009.
Available at https://www.nemi.gov or from
James Eaton, H & E Testing Laboratory, 221
State Street, Augusta, ME 04333. (207) 287–
2727.
8 Systea Easy (1-Reagent). ‘‘Systea Easy (1Reagent) Nitrate Method,’’ February 4, 2009.
Available at https://www.nemi.gov or from
Systea Scientific, LLC., 900 Jorie Blvd., Suite
35, Oak Brook, IL 60523.
9 EPA Method 524.3, Version 1.0.
‘‘Measurement of Purgeable Organic
Compounds in Water by Capillary Column
Gas Chromatography/Mass Spectrometry,’’
June 2009. EPA 815–B–09–009. Available at
https://epa.gov/safewater/methods/
analyticalmethods_ogwdw.html.
10 Mitchell Method M5271, Revision 1.1.
‘‘Determination of Turbidity by Laser
Nephelometry,’’ March 5, 2009. Available at
https://www.nemi.gov or from Leck Mitchell,
PhD, PE, 656 Independence Valley Dr., Grand
Junction, CO 81507.
11 Mitchell Method M5331, Revision 1.1.
‘‘Determination of Turbidity by LED
Nephelometry,’’ March 5, 2009. Available at
VerDate Nov<24>2008
EPA method
Fmt 4700
Sfmt 4700
on the suspension date or for further
information, contact David Stearrett,
Mitigation Directorate, Federal
Emergency Management Agency, 500 C
Street, SW., Washington, DC 20472,
(202) 646–2953.
SUPPLEMENTARY INFORMATION: The NFIP
enables property owners to purchase
flood insurance which is generally not
otherwise available. In return,
communities agree to adopt and
administer local floodplain management
aimed at protecting lives and new
construction from future flooding.
Section 1315 of the National Flood
Insurance Act of 1968, as amended, 42
U.S.C. 4022, prohibits flood insurance
coverage as authorized under the NFIP,
42 U.S.C. 4001 et seq.; unless an
appropriate public body adopts
adequate floodplain management
measures with effective enforcement
measures. The communities listed in
this document no longer meet that
statutory requirement for compliance
with program regulations, 44 CFR part
59. Accordingly, the communities will
be suspended on the effective date in
the third column. As of that date, flood
insurance will no longer be available in
the community. However, some of these
communities may adopt and submit the
required documentation of legally
enforceable floodplain management
measures after this rule is published but
prior to the actual suspension date.
These communities will not be
suspended and will continue their
eligibility for the sale of insurance. A
notice withdrawing the suspension of
the communities will be published in
the Federal Register.
In addition, FEMA has identified the
Special Flood Hazard Areas (SFHAs) in
these communities by publishing a
Flood Insurance Rate Map (FIRM). The
date of the FIRM, if one has been
published, is indicated in the fourth
column of the table. No direct Federal
financial assistance (except assistance
pursuant to the Robert T. Stafford
Disaster Relief and Emergency
Assistance Act not in connection with a
flood) may legally be provided for
construction or acquisition of buildings
E:\FR\FM\03AUR1.SGM
03AUR1
Agencies
[Federal Register Volume 74, Number 147 (Monday, August 3, 2009)]
[Rules and Regulations]
[Pages 38348-38358]
From the Federal Register Online via the Government Printing Office [www.gpo.gov]
[FR Doc No: E9-18361]
-----------------------------------------------------------------------
ENVIRONMENTAL PROTECTION AGENCY
40 CFR Part 141
[EPA-HQ-OW-2009-0345; FRL-8930-8]
Expedited Approval of Alternative Test Procedures for the
Analysis of Contaminants Under the Safe Drinking Water Act; Analysis
and Sampling Procedures
AGENCY: Environmental Protection Agency (EPA).
ACTION: Final rule.
-----------------------------------------------------------------------
SUMMARY: This action announces the Environmental Protection Agency's
(EPA's) approval of alternative testing methods for use in measuring
the levels of contaminants in drinking water and determining compliance
with national primary drinking water regulations. The Safe Drinking
Water Act (SDWA) authorizes EPA to approve the use of alternative
testing methods through publication in the Federal Register. EPA is
using this streamlined authority to make six additional methods
available for analyzing drinking water samples required by regulation.
This expedited approach provides public water systems, laboratories,
and primacy agencies with more timely access to new
[[Page 38349]]
measurement techniques and greater flexibility in the selection of
analytical methods, thereby reducing monitoring costs while maintaining
public health protection.
DATES: This action is effective August 3, 2009.
FOR FURTHER INFORMATION CONTACT: Safe Drinking Water Hotline (800) 426-
4791 or Patricia Snyder Fair, Technical Support Center, Office of
Ground Water and Drinking Water (MS 140), Environmental Protection
Agency, 26 West Martin Luther King Drive, Cincinnati, OH 45268;
telephone number: (513) 569-7937; e-mail address: fair.pat@epa.gov.
SUPPLEMENTARY INFORMATION:
I. General Information
A. Does This Action Apply to Me?
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 SDWA may also measure
contaminants in water samples. When EPA sets a monitoring requirement
in its national primary drinking water regulations for a given
contaminant, the Agency also establishes in the regulations
standardized test procedures for analysis of the contaminant. This
action makes alternative testing methods available for particular
drinking water contaminants beyond the testing methods currently
established in the regulations. EPA is providing public water systems
required to test water samples with a choice of using either a test
procedure already established in the existing regulations or an
alternative test procedure that has been approved in this action.
Categories and entities that may ultimately be affected by this action
include:
------------------------------------------------------------------------
Examples of
Category potentially regulated NAICS \1\
entities
------------------------------------------------------------------------
State, Local, & Tribal Governments. States, local and 924110
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.
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 exhaustive, but rather provides a guide for
readers regarding entities likely to be affected by this action. This
table lists the types of entities that EPA is now aware could
potentially be affected by this action. Other types of entities not
listed in the table could also be impacted. To determine whether your
facility is affected 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 person listed in the
preceding FOR FURTHER INFORMATION CONTACT section.
B. How Can I Get Copies of This Document and Other Related Information?
1. Docket. EPA established a docket for this action under Docket ID
No. EPA-HQ-OW-2009-0345. Publicly available docket materials are
available either electronically through www.regulations.gov or in hard
copy at the Water Docket in the EPA Docket Center, (EPA/DC) EPA West,
Room 3334, 1301 Constitution Ave., NW., Washington, DC. Copyrighted
materials are available only in hard copy. The EPA Docket Center 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 for the Water
Docket is (202) 566-2426.
2. Electronic Access. You may access this Federal Register document
electronically through the EPA Internet under the ``Federal Register''
listings at https://www.epa.gov/fedrgstr/.
Abbreviations and Acronyms Used in This Action
CFR: Code of Federal Regulations
DBCP: Dibromochloropropane
EDB: Ethylene Dibromide
EPA: Environmental Protection Agency
GC: Gas Chromatography
LED: Light-Emitting Diode
MS: Mass Spectrometry
NEMI: National Environmental Methods Index
nm: Nanometers
SDWA: Safe Drinking Water Act
Table of Contents
I. General Information
A. Does This Action Apply to Me?
B. How Can I Get Copies of This Document and Other Related
Information?
II. Background
A. What Is the Purpose of This Action?
B. What Is the Basis for This Action?
III. Summary of Approvals
A. Methods Developed by EPA
B. Methods Developed by Vendors
IV. Statutory and Executive Order Reviews
V. References
II. Background
A. What Is the Purpose of This Action?
In this action, EPA is approving six analytical methods for
determining contaminant concentrations in samples collected under SDWA.
Regulated parties required to sample and monitor may use either the
testing methods already established in existing regulations or the
alternative testing methods being approved in this action. The new
methods are listed in Appendix A to Subpart C in 40 CFR 141 and on
EPA's drinking water methods Web site at https://www.epa.gov/safewater/methods/analyticalmethods_expedited.html.
B. What Is the Basis for This Action?
When EPA determines an alternative analytical method is ``equally
effective'' (i.e., as effective as a method that has already been
promulgated in the regulations), SDWA allows EPA to approve the use of
the alternative method through publication in the Federal Register. See
Section 1401(1) of SDWA. EPA is using this streamlined approval
authority to make six additional methods available for determining
contaminant concentrations in samples collected under SDWA. EPA has
determined that, for each contaminant or group of contaminants listed
in Section III, the additional testing methods being approved in this
action are equally as effective as one or more of the testing methods
already established in the regulations for those contaminants. Section
1401(1) states that the newly approved methods ``shall be treated as
[[Page 38350]]
an alternative for public water systems to the quality control and
testing procedures listed in the regulation.'' Accordingly, this action
makes these additional (and optional) six analytical methods legally
available for meeting EPA's monitoring requirements.
This action does not add regulatory language, but does, for
informational purposes, update an appendix to the regulations at 40 CFR
part 141 that lists all methods approved under Section 1401(1) of SDWA.
Accordingly, while this action is not a rule, it is updating CFR text
and therefore is being published in the ``Final Rules'' section of this
Federal Register.
EPA described this expedited methods approval process in an April
10, 2007, Federal Register notice (72 FR 17902) (USEPA 2007) and
announced its intent to begin using the process. EPA published the
first set of approvals in a June 3, 2008, Federal Register notice (73
FR 31616) (USEPA 2008) and added Appendix A to 40 CFR Part 141, Subpart
C. This action adds six additional methods to Appendix A to Subpart C.
III. Summary of Approvals
EPA is approving six methods that are equally effective relative to
methods previously promulgated in the regulations. By means of this
notice, these six methods are added to Appendix A of 40 CFR Part 141,
Subpart C. For convenience of the reader, the revised Appendix A in its
entirety is shown below. However, the only change made to Appendix A
through this action is the inclusion of these six additional methods as
described in this preamble.
A. Methods Developed by EPA
EPA Method 524.3, Version 1.0. This is a gas chromatography/mass
spectrometry (GC/MS) method for the determination of purgeable organic
compounds in finished drinking waters. The method analytes are purged
from the water sample using helium and trapped on a sorbent material.
After purging, the trap is heated and back flushed with helium to
transfer the analytes to a capillary GC column. Compounds eluting from
the GC are directed into a mass spectrometer for mass analysis and
detection. The analytes are identified by comparing the acquired mass
spectra and retention times to reference spectra and retention times
for calibration standards acquired under identical GC/MS conditions.
The concentration of each target analyte is calculated using the
internal standard technique and response curves obtained via procedural
calibration. The expansion of the method to include the option of
selective ion monitoring makes this method sufficiently sensitive to
measure dibromochloropropane (DBCP) and ethylene dibromide (EDB) at the
concentrations required for drinking water compliance monitoring.
EPA Method 524.3 is an updated version of EPA Method 524.2,
Revision 4.1 (USEPA 1995a), which is currently approved for analyses of
compliance samples for 21 volatile organic contaminants and total
trihalomethanes. The method development work is described in the method
research summary (Zaffiro et al. 2009). The advantages of the new
method include:
Use of maleic acid, a common food preservative, to
preserve samples, eliminating the requirement to ship a hazardous
reagent (hydrochloric acid) to the field;
Incorporation of features that allow users to take
advantage of modern instrumentation to improve speed and data quality;
Increased flexibility in selection of method operating
parameters; and
Addition of Method 524.3 as an approved method for DBCP
and EDB.
Approved methods for volatile organic contaminants and total
trihalomethanes are listed at 40 CFR 141.24(e). EPA Methods 502.2;
Revision 2.1 (USEPA 1995b) and 524.2; Revision 4.1 (USEPA 1995a) are
approved for benzene; carbon tetrachloride; chlorobenzene; 1,2-
dichlorobenzene; 1,4-dichlorobenzene; 1,2-dichloroethane; cis-
dichloroethylene; trans-dichloroethylene; dichloromethane; 1,2-
dichloropropane; ethylbenzene; styrene; tetrachloroethylene; 1,1,1-
trichloroethane; trichloroethylene; toluene; 1,2,4-trichlorobenzene;
1,1-dichloroethylene; 1,1,2-trichlorethane; vinyl chloride; xylenes
(total--measured as sum of o-xylene; m-xylene and p-xylene); and total
trihalomethanes (sum of chloroform; bromodichloromethane;
dibromochloromethane; and bromoform). EPA Method 551.1 (USEPA 1995c) is
approved for carbon tetrachloride; tetrachloroethylene; 1,1,1-
trichloroethane; trichloroethylene; EDB; DBCP; and total
trihalomethanes. EPA Method 504.1, Revision 1.1 (USEPA 1995d) is
approved for EDB and DBCP. Approved methods for total trihalomethanes
are also listed at 40 CFR 141.131(b)(1). For each of the 24
contaminants, the performance characteristics of EPA Method 524.3 were
compared to the characteristics of each of the methods currently listed
in the regulations as approved for that contaminant (Munch 2009). EPA
has determined that, for each of the 24 contaminants, EPA Method 524.3
is equally as effective for measuring the contaminant as the methods
currently listed in the regulations as approved for that contaminant.
The basis for this determination is discussed in Munch 2009. EPA is
therefore approving use of Method 524.3 for the above named 24
contaminants when analyzing drinking water compliance samples.
EPA Method 524.3 Version 1.0 (USEPA 2009) can be accessed and
downloaded directly on-line at https://epa.gov/safewater/methods/analyticalmethods_ogwdw.html.
B. Methods Developed by Vendors
1. Mitchell Method M5271. Mitchell Method M5271 (Mitchell 2009a)
uses laser nephelometry to measure turbidity in drinking water. The
method is based on a comparison of the intensity of light scattered by
the sample under defined conditions with the intensity of light
scattered by a standard reference suspension. Readings are made using
an on-line laser nephelometer with the following design criteria:
Laser light source is monochromatic operated at a nominal
wavelength of 650 30nm;
Incident radiation and any convergence does not exceed
1.5 degrees in the measurement area;
Distance traversed by incident light and scattered light
does not exceed 10cm;
Detector/light receiver is centered at 90 1.5
degrees to the incident light path and the light cone does not exceed
30 degrees from 90 degrees; and
Instrument incorporates a bubble trap and anti-fog
windows. Sensor is horizontal and the windows are vertical. Windows are
immersed in the sample stream.
Four approved methods for turbidity are listed at 40 CFR
141.74(a)(1). The performance characteristics of Mitchell Method M5271
were compared to the performance characteristics of approved EPA Method
180.1 (USEPA 1993a). The validation study report (Mitchell 2008a)
summarizes the results obtained from the turbidimeters placed in series
at three different public water systems. One water system used ground
water and the other two plants used surface water sources. Measurements
included at least one filter backwash at each of the surface water
plants.
EPA has determined that the Mitchell Method M5271 is equally
effective relative to EPA Method 180.1 that is already promulgated in
the regulations at 40 CFR 141.74(a)(1). The basis for this
determination is discussed in Wendelken 2009a. Therefore, EPA is
approving the Mitchell Method M5271 for determining turbidity in
drinking
[[Page 38351]]
water. A copy of the method can be downloaded from the National
Environmental Methods Index (NEMI) at https://www.nemi.gov or obtained
by contacting Leck Mitchell, PhD, PE, 656 Independence Valley Dr.,
Grand Junction, CO 81507.
2. Mitchell Method M5331. Mitchell Method M5331 (Mitchell 2009b)
uses light-emitting diode (LED) nephelometry to measure turbidity in
drinking water. The method is based on a comparison of the intensity of
light scattered by the sample under defined conditions with the
intensity of light scattered by a standard reference suspension.
Readings are made using an on-line LED nephelometer with the following
design criteria:
LED light source is monochromatic operated at a nominal
wavelength of 525 15nm;
Incident radiation and any convergence does not exceed
1.5 degrees in the measurement area;
Distance traversed by incident light and scattered light
does not exceed 10cm;
Detector/light receiver is centered at 90 1.5
degrees to the incident light path and the light cone does not exceed
30 degrees from 90 degrees; and
Instrument incorporates a bubble trap and anti-fog
windows. Sensor is horizontal and the windows are vertical. Windows are
immersed in the sample stream.
Four approved methods for turbidity are listed at 40 CFR
141.74(a)(1). The performance characteristics of Mitchell Method M5331
were compared to the performance characteristics of approved EPA Method
180.1 (USEPA 1993a). The validation study report (Mitchell 2008b)
summarizes the results obtained from the turbidimeters placed in series
at three different public water systems. One water system used ground
water and the other two plants used surface water sources. Measurements
included at least one filter backwash at each of the surface water
plants.
EPA has determined that the Mitchell Method M5331 is equally
effective relative to EPA Method 180.1 that is already promulgated in
the regulations at 40 CFR 141.74(a)(1). The basis for this
determination is discussed in Wendelken 2009b. Therefore, EPA is
approving it for determining turbidity in drinking water. A copy of the
method can be downloaded from NEMI at https://www.nemi.gov or obtained
from Leck Mitchell, PhD, PE, 656 Independence Valley Dr., Grand
Junction, CO 81507.
3. Orion Method AQ4500. Thermo Scientific's Orion Method AQ4500
(Thermo Scientific 2009) uses LED nephelometry to measure turbidity in
drinking water. The method is based on a comparison of the intensity of
light scattered by the sample at 90 degrees to the beam path with the
intensity of light scattered by a standard reference suspension.
Readings are made using a portable LED nephelometer with the following
design criteria:
White LED light source emits broadband light having peak
intensities in the 400nm to 600nm range;
Distance traversed by incident light and scattered light
does not exceed 10cm;
Detector/light receiver is centered at 90 degrees to the
incident light path and the light cone does not exceed 30
degrees from 90 degrees. The detector has spectral peak response
between 400nm and 600nm;
Pulsed light allows for synchronous detection, a technique
by which ambient stray light leakage, as well as other electronic
induced errors, are effectively cancelled out; and
Color compensation is achieved using a dual-beam system
with two photo detectors.
Four approved methods for turbidity are listed at 40 CFR
141.74(a)(1). The performance characteristics of Thermo Scientific's
Orion Method AQ4500 were compared to the performance characteristics of
EPA Method 180.1 (USEPA 1993a) listed at 40 CFR 141.74(a)(1) for
measurement of turbidity. Two rounds of testing were conducted
(Wendelken 2009c). The first was an ASTM round robin study comparing
results from analyses of 28 samples of various types using
turbidimeters with tungsten filament light sources as specified in EPA
Method 180.1 and white LEDs as specified in Thermo Scientific Orion
Method AQ4500. A second study involved demonstration of performance at
turbidities below 2 nephelometric turbidity units.
EPA has determined that Thermo Scientific's Orion Method AQ4500 is
equally effective relative to EPA Method 180.1, which is already
promulgated in the regulations at 40 CFR 141.74(a)(1). The basis for
this determination is discussed in Wendelken 2009c. Therefore, EPA is
approving Method AQ4500 for the measurement of turbidity in drinking
water. A copy of the method can be downloaded from NEMI at https://www.nemi.gov or obtained from Thermo Scientific, 166 Cummings Center,
Beverly, MA 01915, Phone: (800) 225-1480, www.thermo.com.
4. Systea Easy (1-Reagent). Systea Scientific, LLC's Systea Easy
(1-Reagent) Nitrate Method uses automated discreet analysis by
spectrophotometry to determine concentrations of nitrate and nitrite
combined or individually in drinking water. The method involves the
following steps:
Reduction of nitrate in a sample to nitrite using a non-
hazardous proprietary reagent;
Diazotizing the nitrite originally in the sample plus the
reduced nitrate with sulfanilamide followed by coupling with N-(1-
napthyl)ethylenediamine dihydrochloride under acidic conditions to form
a highly colored azo dye;
Colorimetric determination in which the absorbance of
color at 546nm is directly proportional to the concentration of the
nitrite plus the reduced nitrate in the sample;
Measurement of nitrite individually by analysis of the
sample while eliminating the reduction step; and
Subtraction of the nitrite value from that of the combined
nitrate plus nitrite value to determine nitrate individually.
Approved methods for nitrate and nitrite are listed at 40 CFR
141.23(k)(1). An inter-laboratory study (Systea Scientific, LLC. 2008)
was conducted to compare the performance characteristics of the Systea
Easy (1-Reagent) Nitrate Method to the characteristics of the EPA
Method 353.2 (USEPA 1993b) and Standard Method 4500-
NO3- F-00 (APHA 1997), which are listed at 40 CFR
141.23(k)(1) for nitrate and nitrite. Ten laboratories analyzed a
variety of sample matrices using approved methods. The samples were
also analyzed using the Systea Easy (1-Reagent) Nitrate Method.
EPA has determined that the Systea Easy (1-Reagent) Nitrate Method
is equally effective relative to EPA Method 353.2 and Standard Method
4500-NO3- F-00, which are already promulgated in
the regulations. The basis for this determination is discussed in
Wendelken 2009d. The method is a ``green'' alternative to other
approved methods, which use cadmium, a known carcinogen, for the
reduction of nitrate to nitrite. EPA is approving this method for
determining nitrate and nitrite concentrations in drinking water to
comply with 40 CFR 141.23.
Systea Easy (1-Reagent) Nitrate Method (Systea Scientific, LLC.
2009) can be downloaded from NEMI at https://www.nemi.gov or obtained
from Systea Scientific, LLC, 900 Jorie Blvd., Suite 35, Oak Brook, IL
60523, Phone: (630) 645-0600.
5. Method ME355.01. ``Determination of Cyanide in Drinking Water by
GC/MS Headspace'' (Eaton 2009) uses direct headspace injection after
acidification followed by Gas Chromatography/Mass
[[Page 38352]]
Spectrometry (GC/MS) to determine the concentration of cyanide, as free
cyanide, in drinking water. The method involves the following steps:
Acidification of the sample;
Heating the sample to 60 degrees Celsius with agitation;
Direct injection of 1 milliliter of headspace onto the
nitrogen cooled cryotrap; and
Analysis using temperature programmed GC/MS.
The performance characteristics of Method ME355.01 were determined
in three laboratories by replicate analyses of fortified samples
(Wendelken 2009e). The results were compared to the characteristics of
EPA Method 335.4 (USEPA 1993c) and Standard Method 4500-CN-
F-99 (APHA 1999) listed at 40 CFR 141.23(k)(1) for cyanide. EPA has
determined that Method ME355.01 is equally effective relative to each
of these two methods. The basis for this determination is discussed in
Wendelken 2009e. Therefore, EPA is approving this method for
determining cyanide concentrations in drinking water to comply with 40
CFR 141.23.
Method ME335.01 can be downloaded from NEMI at https://www.nemi.gov
or obtained from James Eaton, PhD, H & E Testing Laboratory, 221 State
Street, Augusta, ME 04333, Phone: (207) 187-2727.
IV. Statutory and Executive Order Reviews
As noted above, under the terms of SDWA Section 1401(1), this
streamlined method approval action is not a rule. Accordingly, the
Congressional Review Act, 5 U.S.C. 801 et seq., as added by the Small
Business Regulatory Enforcement Fairness Act of 1996, does not apply
because this action is not a rule for purposes of 5 U.S.C. 804(3).
Similarly, this action is not subject to the Regulatory Flexibility Act
because it is not subject to notice and comment requirements under the
Administrative Procedure Act or any other statute. In addition, because
this approval action is not a rule but simply makes alternative
(optional) testing methods available for monitoring under SDWA, EPA has
concluded that other statutes and executive orders generally applicable
to rulemaking do not apply to this approval action.
V. References
American Public Health Association (APHA), 2000. Standard Method
4500-NO3- F-00. Automated Cadmium Reduction
Method. Approved by Standard Methods Committee 2000. Standard Methods
Online. (Available at https://www.standardmethods.org.)
American Public Health Association (APHA), 1999. Standard Method
4500-CN- F-99. Cyanide-Selective Electrode Method. Approved
by Standard Methods Committee 1999. Standard Methods Online. (Available
at https://www.standardmethods.org.)
Eaton, J. 2009. Method ME355.01, Revision 1.0. Determination of
Cyanide in Drinking Water by GC/MS Headspace. May 26, 2009. H & E
Testing Laboratory, 221 State Street, Augusta, ME 04333. (Available at
https://www.nemi.gov.)
Mitchell, L. and Mitchell, P., 2008a. Mitchell ATP Submission for
Changes in Method 180.1 Using Laser Determination of Turbidity by
Nephelometry, Mitchell Method M5271, Validation Study Report, Revision
1.0, July 31, 2008. 656 Independence Valley Dr., Grand Junction, CO
81507.
Mitchell, L. and Mitchell, P., 2008b. Mitchell ATP Submission for
Changes in Method 180.1 Using LED Determination of Turbidity by
Nephelometry, Mitchell Method M5331, Validation Study Report, Revision
1.0, July 31, 2008. 656 Independence Valley Dr., Grand Junction, CO
81507.
Mitchell, L. and Mitchell, P., 2009a. Mitchell Method M5271,
Revision 1.1. Determination of Turbidity by Laser Nephelometry, March
5, 2009. Leck Mitchell, PhD, PE, 656 Independence Valley Dr., Grand
Junction, CO 81507. (Available at https://www.nemi.gov.)
Mitchell, L. and Mitchell, P., 2009b. Mitchell Method M5331,
Revision 1.1. Determination of Turbidity by LED Nephelometry, March 5,
2009. Leck Mitchell, PhD, PE, 656 Independence Valley Dr., Grand
Junction, CO 81507. (Available at https://www.nemi.gov.)
Munch, D., 2009. Memo to the record describing basis for expedited
approval of EPA Method 524.3. May 22, 2009.
Systea Scientific, LLC., 2008. Validation Study Report for New
Method Approval of Nitrate Analysis in Wastewater and Drinking Water
Utilizing Systea Scientific, LLC Non-Hazardous Proprietary Reagent R1,
Systea Easy (1-Reagent) Nitrate 0.050-10 mg/L. September 15, 2008. 900
Jorie Blvd., Suite 35, Oak Brook, IL 60523.
Systea Scientific, LLC., 2009. Systea Easy (1-Reagent) Nitrate
Method, February 4, 2009. 900 Jorie Blvd., Suite 35, Oak Brook, IL
60523. (Available at https://www.nemi.gov.)
Thermo Scientific, 2009. Orion Method AQ4500, Revision 1.0.
Determination of Turbidity by LED Nephelometry, May 8, 2009. 166
Cummings Center, Beverly, MA 01915. (Available at https://www.nemi.gov.)
USEPA. 1993a. EPA Method 180.1, Revision 2.0, ``Determination of
Turbidity by Nephelometry'' in Methods for the Determination of
Inorganic Substances in Environmental Samples, EPA/600/R-93/100.
(Available at https://www.nemi.gov.)
USEPA. 1993b. EPA Method 353.2, Revision 2.0, ``Determination of
Nitrate-Nitrite Nitrogen by Automated Colorimetry'' in Methods for the
Determination of Inorganic Substances in Environmental Samples, EPA/
600/R-93/100. (Available at https://www.nemi.gov.)
USEPA. 1993c. EPA Method 335.4, Revision 1.0, ``Determination of
Total Cyanide by Semi-Automated Colorimetry'' in Methods for the
Determination of Inorganic Substances in Environmental Samples, EPA/
600/R-93/100. (Available at https://www.nemi.gov.)
USEPA. 1995a. EPA Method 524.2, Revision 4.1, ``Measurement of
Purgeable Organic Compounds in Water by Capillary Column Gas
Chromatography/Mass Spectrometry'' in Methods for the Determination of
Organic Compounds in Drinking Water--Supplement III, EPA/600/R-95-131.
(Available at https://www.nemi.gov.)
USEPA. 1995b. EPA Method 502.2, Revision 2.1, ``Volatile Organic
Compounds in Water by Purge and Trap Capillary Column Gas
Chromatography with Photoionization and Electrolytic Conductivity
Detectors in Series'' in Methods for the Determination of Organic
Compounds in Drinking Water--Supplement III, EPA/600/R-95-131.
(Available at https://www.nemi.gov.)
USEPA. 1995c. EPA Method 551.1, Revision 1.0, ``Determination of
Chlorination Disinfection Byproducts, Chlorinated Solvents, and
Halogenated Pesticides/Herbicides in Drinking Water by Liquid-Liquid
Extraction and Gas Chromatography with Electron-Capture Detection'' in
Methods for the Determination of Organic Compounds in Drinking Water--
Supplement III, EPA/600/R-95-131. (Available at https://www.nemi.gov.)
USEPA. 1995d. EPA Method 504.1, Revision 1.1, ``1,2-Dibromoethane
(EDB), 1,2-Dibromo-3-Chloro-Propane (DBCP), and 1,2,3-Trichloropropane
(123TCP) in Water by Microextraction and Gas Chromatography'' in
Methods for the Determination of Organic Compounds in Drinking Water--
Supplement III, EPA/600/R-95-131. (Available at https://www.nemi.gov.)
USEPA. 2007. Expedited Approval of Test Procedures for the Analysis
of Contaminants Under the Safe Drinking Water Act; Analysis and
Sampling Procedures. 72 FR 17902. April 10, 2007.
[[Page 38353]]
USEPA. 2008. Expedited Approval of Alternative Test Procedures for
the Analysis of Contaminants Under the Safe Drinking Water Act;
Analysis and Sampling Procedures. 73 FR 31616. June 3, 2008.
USEPA. 2009. EPA Method 524.3 Version 1.0. Measurement of Purgeable
Organic Compounds in Water by Capillary Column Gas Chromatography/Mass
Spectrometry, EPA 815-B-09-009. June 2009. (Available at https://epa.gov/safewater/methods/analyticalmethods_ogwdw.html.)
Wendelken, S., 2009a. Memo to the record describing basis for
expedited approval of Mitchell Method M5271. May 29, 2009.
Wendelken, S., 2009b. Memo to the record describing basis for
expedited approval of Mitchell Method M5331. May 29, 2009.
Wendelken, S., 2009c. Memo to the record describing ATP evaluation
of Thermo Scientific/Orion Method AQ4500, Revision 1.0 and basis for
expedited approval. May 29, 2009.
Wendelken, S., 2009d. Memo to the record describing basis for
expedited approval of Systea Easy (1-Reagent) Nitrate Method. May 29,
2009.
Wendelken, S., 2009e. Memo to the record describing ATP evaluation
of Method ME355.01 and basis for expedited approval. May 29, 2009.
Zaffiro, A.D, Prakash, B. and Zimmerman, M., 2009. EPA Method 524.3
Research Summary, Shaw Environmental, Cincinnati OH. June 2009.
List of Subjects in 40 CFR Part 141
Environmental protection, Chemicals, Indians--lands,
Intergovernmental relations, Radiation protection, Reporting and
recordkeeping requirements, Water supply.
Dated: July 9, 2009.
Michael H. Shapiro,
Acting Assistant Administrator, Office of Water.
0
For the reasons stated in the preamble, 40 CFR part 141 is amended as
follows:
PART 141--NATIONAL PRIMARY DRINKING WATER REGULATIONS
0
1. The authority citation for part 141 continues to read as follows:
Authority: 42 U.S.C. 300f, 300g-1, 300j-4, and 300j-9.
0
2. Subpart C is amended by revising Appendix A to read as follows:
Appendix A to Subpart C of Part 141--Alternative Testing Methods
Approved for Analyses Under the Safe Drinking Water Act
Only the editions stated in the following table are approved.
Alternative Testing Methods for Contaminants Listed at 40 CFR
141.21(f)(3)
------------------------------------------------------------------------
Organism Methodology SM 21st edition \1\
------------------------------------------------------------------------
Total Coliforms.............. Total Coliform 9221 A, B
Fermentation
Technique.
Total Coliform 9222 A, B, C
Membrane Filter
Technique.
Presence-Absence 9221 D
(P-A) Coliform
Test.
ONPG-MUG Test... 9223
------------------------------------------------------------------------
Alternative Testing Methods for Contaminants Listed at 40 CFR 141.23(k)(1)
--------------------------------------------------------------------------------------------------------------------------------------------------------
Contaminant Methodology EPA method SM 21st edition \1\ SM online \3\ ASTM \4\ Other
--------------------------------------------------------------------------------------------------------------------------------------------------------
Alkalinity................... Titrimetric..... 2320 B
Antimony..................... Atomic 3113 B
Absorption;
Furnace.
Axially viewed 200.5,
inductively Revision 4.2
coupled plasma- \2\.
atomic emission
spectrometry
(AVICP-AES).
Arsenic...................... Atomic 3113 B
Absorption;
Furnace.
Hydride Atomic 3114 B
Absorption.
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Barium....................... Inductively 3120 B
Coupled Plasma.
Atomic 3111 D
Absorption;
Direct.
Atomic 3113 B
Absorption;
Furnace.
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Beryllium.................... Inductively 3120 B
Coupled Plasma.
Atomic 3113 B
Absorption;
Furnace.
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Cadmium...................... Atomic 3113 B
Absorption;
Furnace.
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Calcium...................... EDTA titrimetric 3500-Ca B
Atomic 3111 B
Absorption;
Direct
Aspiration.
Inductively 3120 B
Coupled Plasma.
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Chromium..................... Inductively 3120 B
Coupled Plasma.
Atomic 3113 B
Absorption;
Furnace.
[[Page 38354]]
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Copper....................... Atomic 3113 B
Absorption;
Furnace.
Atomic 3111 B
Absorption;
Direct
Aspiration.
Inductively 3120 B
Coupled Plasma.
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Conductivity................. Conductance..... 2510 B
Cyanide...................... Manual .................... .................... D2036-06 A
Distillation
followed by.
Spectrophotome 4500-CN- G .................... D2036-06 B
tric, Amenable
Spectrophotome 4500-CN- E .................... D2036-06 A
tric Manual
Selective 4500-CN- F
Electrode.
Gas .................... .................... .................... ME355.01 \7\
Chromatography/
Mass
Spectrometry
Headspace.
Fluoride..................... Ion 4110 B
Chromatography.
Manual 4500-F- B, D
Distillation;
Colorimetric
SPADNS.
Manual Electrode 4500-F- C .................... D1179-04 B
Automated 4500-F- E
Alizarin.
Lead......................... Atomic 3113 B
Absorption;
Furnace.
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Magnesium.................... Atomic 3111 B
Absorption.
Inductively 3120 B
Coupled Plasma.
Complexation 3500-Mg B
Titrimetric
Methods.
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Mercury...................... Manual, Cold 3112 B
Vapor.
Nickel....................... Inductively 3120 B
Coupled Plasma.
Atomic 3111 B
Absorption;
Direct.
Atomic 3113 B
Absorption;
Furnace.
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Nitrate...................... Ion 4110 B
Chromatography.
Automated 4500-NO3- F
Cadmium
Reduction.
Manual Cadmium 4500-NO3- E
Reduction.
Ion Selective 4500-NO3- D
Electrode.
Reduction/ .................... .................... .................... Systea Easy
Colorimetric. (1-Reagent) \8\
Nitrite...................... Ion 4110 B
Chromatography.
Automated 4500-NO3- F
Cadmium
Reduction.
Manual Cadmium 4500-NO3- E
Reduction.
Spectrophotometr 4500-NO2- B
ic.
Reduction/ .................... .................... .................... Systea Easy
Colorimetric. (1-Reagent) \8\
Orthophosphate............... Ion 4110 B
Chromatography.
Colorimetric, 4500-P E 4500-P E-99
ascorbic acid,
single reagent.
Colorimetric, 4500-P F 4500-P F-99
Automated,
Ascorbic Acid.
pH........................... Electrometric... 4500-H\+\ B
Selenium..................... Hydride-Atomic 3114 B
Absorption.
Atomic 3113 B
Absorption;
Furnace.
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Silica....................... Colorimetric.... .................... .................... D859-05
Molybdosilicate. 4500-SiO2 C
Heteropoly blue. 4500-SiO2 D
Automated for 4500-SiO2 E
Molybdate-
reactive Silica.
[[Page 38355]]
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Inductively 3120 B
Coupled Plasma.
Sodium....................... Atomic 3111 B
Absorption;
Direct
Aspiration.
Axially viewed 200.5, Revision
inductively 4.2.
coupled plasma-
atomic emission
spectrometry
(AVICP-AES).
Temperature.................. Thermometric.... 2550
--------------------------------------------------------------------------------------------------------------------------------------------------------
Alternative Testing Methods for Contaminants Listed at 40 CFR 141.24(e)(1)
----------------------------------------------------------------------------------------------------------------
SM 21st edition
Contaminant Methodology EPA method \1\ SM online \3\
----------------------------------------------------------------------------------------------------------------
Benzene...................... Purge & Trap/Gas 524.3 \9\ ................... ..................
Chromatography/Mass
Spectrometry.
Carbon tetrachloride......... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Chlorobenzene................ Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
1,2-Dichlorobenzene.......... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
1,4-Dichlorobenzene.......... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
1,2-Dichloroethane........... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
cis-Dichloroethylene......... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Trans-Dichloroethylene....... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Dichloromethane.............. Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
1,2-Dichloropropane.......... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Ethylbenzene................. Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Styrene...................... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Tetrachloroethylene.......... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
1,1,1-Trichloroethane........ Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Trichloroethylene............ Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Toluene...................... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
1,2,4-Trichlorobenzene....... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
1,1-Dichloroethylene......... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
1,1,2-Trichlorethane......... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Vinyl chloride............... Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Xylenes (total).............. Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Carbofuran................... High-performance ................. 6610 B 6610 B-04
liquid
chromatography
(HPLC) with post-
column
derivatization and
fluorescence
detection.
Dibromochloropropane (DBCP).. Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Ethyl dibromide (EDB)........ Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
Oxamyl....................... High-performance ................. 6610 B 6610 B-04
liquid
chromatography
(HPLC) with post-
column
derivatization and
fluorescence
detection.
Total Trihalomethanes........ Purge & Trap/Gas 524.3 ................... ..................
Chromatography/Mass
Spectrometry.
----------------------------------------------------------------------------------------------------------------
Alternative Testing Methods for Contaminants Listed at 40 CFR 141.25(a)
----------------------------------------------------------------------------------------------------------------
Contaminant Methodology SM 21st edition \1\ ASTM \4\
----------------------------------------------------------------------------------------------------------------
Naturally Occurring:
Gross alpha and beta........... Evaporation........... 7110 B ........................
Gross alpha.................... Coprecipitation....... 7110 C ........................
Radium 226..................... Radon emanation....... 7500-Ra C ........................
Radiochemical......... 7500-Ra B ........................
Radium 228..................... Radiochemical......... 7500-Ra D ........................
Uranium........................ Radiochemical......... 7500-U B ........................
ICP-MS................ D5673-05
Alpha spectrometry.... 7500-U C ........................
Man-Made:
Radioactive Cesium............. Radiochemical......... 7500-Cs B ........................
Gamma Ray Spectrometry 7120 ........................
Radioactive Iodine............. Radiochemical......... 7500-I B
7500-I C
7500-I D
Gamma Ray Spectrometry 7120 ........................
Radioactive Strontium 89, 90... Radiochemical......... 7500-Sr B ........................
Tritium........................ Liquid Scintillation.. 7500-\3\H B ........................
[[Page 38356]]
Gamma Emitters................. Gamma Ray Spectrometry 7120
7500-Cs B
7500-I B ........................
----------------------------------------------------------------------------------------------------------------
Alternative Testing Methods for Contaminants Listed at 40 CFR 141.74(a)(1)
----------------------------------------------------------------------------------------------------------------
Organism Methodology SM 21st edition \1\ Other
----------------------------------------------------------------------------------------------------------------
Total Coliform.................... Total Coliform 9221 A, B, C .............................
Fermentation
Technique.
Total Coliform 9222 A, B, C .............................
Membrane Filter
Technique.
ONPG-MUG Test....... 9223 .............................
Fecal Coliforms................... Fecal Coliform 9221 E .............................
Procedure.
Fecal Coliform 9222 D .............................
Filter Procedure.
Heterotrophic bacteria............ Pour Plate Method... 9215 B .............................
Turbidity......................... Nephelometric Method 2130 B .............................
Laser Nephelometry ....................... Mitchell M5271\10\
(on-line).
LED Nephelometry (on- ....................... Mitchell M5331 \11\
line).
LED Nephelometry ....................... Orion AQ4500 \12\
(portable).
----------------------------------------------------------------------------------------------------------------
Alternative Testing Methods for Disinfectant Residuals Listed at 40 CFR
141.74(a)(2)
------------------------------------------------------------------------
Residual Methodology SM 21st edition \1\
------------------------------------------------------------------------
Free Chlorine................. Amperometric 4500-Cl D
Titration.
DPD Ferrous 4500-Cl F
Titrimetric.
DPD Colorimetric. 4500-Cl G
Syringaldazine 4500-Cl H
(FACTS).
Total Chlorine................ Amperometric 4500-Cl D
Titration.
Amperometric 4500-Cl E
Titration (Low
level
measurement).
DPD Ferrous 4500-Cl F
Titrimetric.
DPD Colorimetric. 4500-Cl G
Iodometric 4500-Cl I
Electrode.
Chlorine Dioxide.............. Amperometric 4500-ClO2 C
Titration.
Amperometric 4500-ClO2 E
Titration.
Ozone......................... Indigo Method.... 4500-O3 B
------------------------------------------------------------------------
Alternative Testing Methods for Contaminants Listed at 40 CFR 141.131(b)(1)
----------------------------------------------------------------------------------------------------------------
Contaminant Methodology EPA method SM 21st edition \1\
----------------------------------------------------------------------------------------------------------------
TTHM............................... P&T/GC/MS............ 524.3 \9\ ............................
HAA5............................... LLE (diazomethane)/GC/ ...................... 6251 B
ECD.
Chlorite--daily monitoring as Amperometric ...................... 4500-ClO2 E
prescribed in 40 CFR Titration.
141.132(b)(2)(i)(A).
----------------------------------------------------------------------------------------------------------------
Alternative Testing Methods for Disinfectant Residuals Listed at 40 CFR
141.131(c)(1)
------------------------------------------------------------------------
Residual Methodology SM 21st edition \1\
------------------------------------------------------------------------
Free Chlorine................ Amperometric 4500-Cl D
Titration.
DPD Ferrous 4500-Cl F
Titrimetric.
DPD Colorimetric 4500-Cl G
Syringaldazine 4500-Cl H
(FACTS).
Combined Chlorine............ Amperometric 4500-Cl D
Titration.
DPD Ferrous 4500-Cl F
Titrimetric.
DPD Colorimetric 4500-Cl G
Total Chlorine............... Amperometric 4500-Cl D
Titration.
Low level 4500-Cl E
Amperometric
Titration.
DPD Ferrous 4500-Cl F
Titrimetric.
DPD Colorimetric 4500-Cl G
Iodometric 4500-Cl I
Electrode.
Chlorine Dioxide............. Amperometric 4500-ClO2 E
Method II.
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[[Page 38357]]
Alternative Testing Methods for Disinfectant Residuals Listed at 40 CFR
141.131(c)(2), If Approved by the State
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Residual Methodology Method
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Free Chlorine................ Test Strips..... Method D99-003 \5\
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Alternative Testing Methods for Parameters Listed at 40 CFR 141.131(d)
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Parameter Methodology SM 21st edition \1\
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Total Organic Carbon (TOC)............... High Temperature Combustion...... 5310 B
Persulfate-Ultraviolet or Heated 5310 C
Persulfate Oxidation.
Wet Oxidation.................... 53