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CFR 136.3(a), Table IB. The test proce- Plasma-Mass Spectrometry,” from dures for the regulated pollutants (ar- “Methods for Determination of Metals senic, cadmium, chromium (total), cop- in Environmental Samples-Suppleper, pH, lead, mercury, TSS, silver, ti- ment I," EPA-600/R-94-111, May 1994, tanium, and zinc) listed in the table to and ASTM Method D 5673–96, “Standthis paragraph are also incorporated by ard Test Method for Elements in Water reference into this regulation. The full by Inductively Coupled Plasma-Mass texts of the test procedures listed in Spectrometry,” from 1999 Annual Book this paragraph are available from the of ASTM Standards, for determination sources indicated in paragraph (b)(2) of of arsenic, cadmium, chromium (total), this section. In addition to those test copper, lead, silver, and zinc. The full procedures incorporated by reference texts of these methods are incorat 40 CFR 136.3(a), Table IB, you may porated by reference into this regulaalso use EPA Method 200.8, “Deter- tion and may be obtained from the mination of Trace Elements in Water sources identified in paragraph (b)(2) of and Wastes by Inductively Coupled this section.

LIST OF APPROVED INORGANIC TEST PROCEDURES

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AA furnace
ICP/AES 15
DCP 15 or
Colorimetric

(Neocuproine) or.
(Bicinchoninate), or

ICP/MS 5. Hydrogen ion (pH), PH units:

Electrometric measure

ment.

Automated electrode 6. Lead—Total, * mg L; Digestion 4 tollowed by

AA direct aspiration 15

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D3559-90(A or B)

239.1

3111 B or C

1-3399-85

974.27.3

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AA furnace

239.2
ICP/AES 15

5200.7
DCP 15
Voltametry
Colorimetric (Dithizone),

or.
ICP/MS

7200.8 7. Mercury-Total, 4 mg/L:

Cold vapor, manual or 245.1
Automated

245.1
8. Residue-nonfilterable (TSS),
ng:

Gravimetric, 103-105–160.2

post washing of res

idue.
9. Silver-Total, mg/L: Diges-
tion 4.12 followed by:

AA direct aspiration 272.1
AA furnace

272.2
ICP/AES

5200.7
DCP, or
ICP/MS

7200.8
10. Titanium-Total, mg/L; Di-
gestion followed by:
AA direct aspiration

283.1 AA furnace, or

283.2 DCP 11. Zinc-Total, 4 mg/L; Digestion followed by:

AA direct aspiration 15 289.1

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289.2
5200.7

3120 B

D4190-82(88)

AA furnace
ICP/AES 15
DCP 15
Colorimetric (Dithizone)

or.
(Zincon), or
ICP/MS

3500-Zn E

(14) (

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Table Notes:

"Methods for Chemical Analysis of Water and Wastes,” Environmental Protection Agency, Environmental Monitoring Systems Laboratory-Cincinnati (EMSL-CI). EPA-600/4-79-020, Revised March 1983 and 1979 where applicable.

2 Fishman, M.J., et al. “Methods for Analysis of Inorganic Substances in Water and Fluvial Sediments," U.S. Department of the Interior, Techniques of Water-Resource Investigations of the U.S. Geological Survey, Denver, CO, Revised 1989

3 "Official Methods of Analysis of the Association of Official Analytical Chemists." methods manual, 15th ed. (1990). 4 For the determination of total metals the sample is not filtered before processing. A digestion procedure is required to solubilize suspended material and to destroy possible organic-metal complexes. Two digestion procedures are given in "Methods for Chemical Analysis of Water and Wastes, 1979 and 1983". One (Section 4.1.3), is a vigorous digestion using nitric acid. A less vigorous digestion using nitric and hydrochloric acids (Section 4.1.4) is preferred; however, the analyst should be cautioned that this mild digestion may not suffice for all samples types. Particularly, if a colorimetric procedure is to be employed, it is necessary to ensure that all organo-metallic bonds be broken so that the metal is in a reactive state. In those situations, the vigorous digestion is to be preferred making certain that at no time does the sample go to dryness. Samples containing large amounts of organic materials may also benefit by this vigorous digestion, however, vigorous digestion with concentrated nitric acid will convert antimony and tin to insoluble oxides and render them unavailable for analysis. Use of ICP/AES as well as determinations for certain elements such as antimony, arsenic, the noble metals, mercury, selenium, silver, tin, and titanium require a modified sample digestion procedure and in all cases the method write-up should be consulted for specific instructions andor cautions. NOTE.-t the digestion procedure for direct aspiration AA included in one of the other approved references is different than the above, the EPA procedure must be used.

Dissolved metals are defined as those constituents which will pass through a 0.45 micron membrane filter. Following filtration of the sample, the referenced procedure for total metals must be followed. Sample digestion of the filtrate for dissolved metals (or digestion of the original sample solution for total metals) may be omitted for AA (direct aspiration or graphite turnace) and ICP analyses, provided the sample solution to be analyzed meets the following criteria:

a. Has a low COD (<20) b. Is visibly transparent with a turbidity measurement of 1 NTU or less c. Is colorless with no perceptible odor, and d. Is of one liquid phase and free of particulate or suspended matter following acidification. 5 EPA Method 200.7, "Inductively Coupled Plasma Atomic Emission Spectrometric Method for Trace Element Analysis of Water and Wastes," from "Methods for Determination of Metals in Environmental Samples-Supplement 1,” EPA-600/R-94–111, May 1994.

6 Standard Methods for the Examination of Water and Wastewater," 18th Edition (1992).

7 EPA Method 200.8, "Determination of Trace Elements in Waters and Wastes by Inductively coupled Plasma-Mass Spectrometry," from "Methods for Determination of Metals in Environmental Samples-Supplement 1," ÉPA-600/R-94–111, May 1994.

5 American National Standard on Photographic Processing Effluents, Apr, 2, 1975. Available from ANSI, 1430 Broadway, New York, NY 10018 * The use of normal and differential pulse voltage ramps to increase sensitivity and resolution is acceptable.

10 Copper, Biocinchoinate Method, Method 8506, Hach Handbook of Water Analysis, 1979, Hach Chemical Company, PO Box 389, Loveland, CO 80537.

11 Hydrogen ion (pH) Automated Electrode Method, Industrial Method Number 378–75WA, October 1976, Bran & Luebbe (Technicon) Autoanalyzer II. Bran & Luebbe Analyzing Technologies, Inc., Elmsford, NY 10523.

12 Approved methods for the analysis of silver in industrial wastewaters at concentrations of 1 mg/L and above are inadequate where silver exists as an inorganic halide. Silver halides such as the bromide and chloride are relatively insoluble in reagents such as nitric acid but are readily soluble in an aqueous butter of sodium thiosultate and sodium hydroxide to pH of 12. Therefore, for levels of silver above 1 mg/L, 20 mL of sample should be diluted to 100 mL by adding 40 mL each of 2 M Na2S2O, and NaOH. Standards should be prepared in the same manner. For levels of silver below 1 mg/l the approved method is satisfactory

13 Zinc, Zincon Method, Method 8009, Hach Handbook of Water Analysis, 1979, pages 2-231 and 2–333, Hach Chemical Company, Loveland, CO 80537.

1* "Direct Current Plasma (DCP) Optical Emission Spectrometric Method for Trace Elemental Analysis of Water and Wastes, Method AES0029," 1986—Revised 1991, Thermo Jarrell Ash Corporation, 27 Forge Parkway, Franklin, MA 02038.

15 "Closed Vessel Microwave Digestion of Wastewater Samples for Determination of Metals,” CEM Corporation, PO, Box 200, Matthews, NC 28106-0200, April 16, 1992. Available from the CEM Corporation.

16 Precision and recovery statements for the atomic absorption direct aspiration and graphite furnace methods, and for the spectrophotometric SDOC method for arsenic are provided in Appendix D of 40 CFR Part 136 and titled, "Precision and Recovery Statements for Methods for Measuring Metals.

1? This method does not include the digestion for solids given in Method 200.8. Not using the solids digestion procedure could affect the determined concentrations. Therefore, this method may not be used for analysis of aqueous samples with suspended solids greater than 1%.

are

(2) The full texts of the methods from the following references which cited in the table in paragraph (b)(1) of this section are incorporated by reference into this regulation and may be obtained from the sources identified. All costs cited are subject to change and must be verified from the indicated sources. The full texts of all the test procedures cited are available for inspection at the Analytical Methods Staff, Office of Water, U.S. Environmental Protection Agency, 1200 Pennsylvania Ave., NW., Washington, DC 20460 or at the National Archives and Records Administration (NARA). For information on the availability of this material at NARA, call 202–741-6030, or go to: http://www.archives.gov/ federal_register/ code_of_federal_regulations/ ibt locations.html.

tion 11, Volumes 11.01 (Water I) and 11.02 (Water II), 1994. [1996 for D5673-96; see Note 17]. American Society for Testing and Materials, 1916 Race Street, Philadelphia, PA 19103.

(4) “Methods for the Determination of Metals in Environmental Samples-Supplement I”, National Exposure Risk Laboratory, Office of Research and Development, U.S. Environmental Protection Agency, Cincinnati, OH 45268, EPA 600 R-94/111, May 1994. [Notes 5 and 7)

(5) "Methods for Determination of Inorganic Substances in Water and Fluvial Sediments," by M.J. Fishman and Linda C. Friedman, Techniques of Water Resources Investigations of the U.S. Geological Survey, Book 5 Chapter A1 (1989). Available from: U.S. Geological Survey, Denver Federal Center, Box 25425, Denver, CO 80225. Cost: $108.75 (subject to change). [Note 2]

(6) "Closed Vessel Microwave Digestion of Wastewater Samples for Determination of Metals," CEM Corporation, P.O. Box 200, Matthews, North Carolina 28106-0200, April 16, 1992. Available from the CEM Corporation. [Note 15)

(7) "Official Methods of Analysis of AOAC-International, 15th Edition," 1990. Price: $359.00. Available from: AOAC-International, 1970 Chain Bridge Rd., Dept. 0742, McLean, VA 22109 0742. [Note 3]

(8) "American National Standard on Photographic Processing Effluents,” April 2, 1975. Available from: American National Standards Institute, 11 West 42nd Street, New York, New York 10036. [Note 8]

(9) Bicinchoninate Method for Copper. Method 8506, Hach Handbook of Water Analysis, 1979, Method and price available from Hach Chemical Company, P.O. Box 300, Loveland, Colorado 80537. [Note 10)

(10) Hydrogen Ion (pH) Automated Electrode Method, Industrial Method Number 378–75WA. October 1976. Bran & Luebbe (Technicon) Auto Analyzer II. Method and

APPENDIX TO $444.12(b)-REFERENCES, SOURCES, COSTS, AND TABLE CITATIONS: (1) “Methods for Chemical Analysis of Water and Wastes," U.S. Environmental Protection Agency, EPA-600/4_79-020, Revised March 1983 and 1979 where applicable. Available from: ORD Publications, CERI, U.S. Environmental Protection Agency, Cincinnati, Ohio 45268. (Note 1]

(2) "Standard Methods for the Examination of Water and Wastewater." Joint Editorial Board, American Public Health Association, American Water Works Association, and Water Environment Federation, 18th Edition, 1992. Available from: American Public Health Association, 1015 15th Street NW, Washington, DC 20005. [Note 6)

(3) "Annual Book of ASTM StandardsWater and Environmental Technology," Sec

price available from Bran & Luebbe Analyzing Technologies, Inc. Elmsford, N.Y. 10523. [Note 11]

(11) Zincon Method for Zinc, Method 8009. Hach Handbook for Water Analysis, 1979. Method and price available from Hach Chemical Company, P.O. Box 389, Loveland, Colorado 80537. [Note 13]

(12) "Direct Current Plasma (DCP) Optical Emission Spectrometric Method for Trace Elemental Analysis of Water and Wastes," Method AES 0029, 1986 Revised 1991, Thermo Jarrell Ash Corporation (508-520-1880), 27 Forge Parkway, Franklin, MA 02038. [Note 14] (65 FR 4381, Jan. 27, 2000, as amended at 65 FR 70315, Nov. 22, 2000; 69 FR 18803, Apr. 9, 2004]

8 444.15 Effluent limitations attainable

by the application of the best avail. able technology economically

achievable (BAT). Except as provided in 40 CFR 125.30 through 125.32, any existing point source subject to this subpart must achieve the following effluent limitations representing the application of BAT: Limitations for arsenic, cadmium, chromium, copper, lead, mercury, silver, titanium and zinc are the same as the corresponding limitation specified in § 444.13.

8 444.16 Pretreatment standards for

existing sources (PSES). Except as provided in 40 CFR 403.7 and 403.13, any source that introduces wastewater pollutants into a POTW must comply with part 403 and achieve the following pretreatment standards:

444.13 Effluent limitations attainable

by the application of the best practicable control technology currently

available (BPT). Except as provided in 40 CFR 125.30 through 125.32, any existing point source subject to this subpart must achieve the following effluent limitations representing the application of BPT:

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EFFLUENT LIMITATIONS ?

Arsenic Cadmium Chromium Copper Lead Mercury Silver Titanium Zinc

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Micrograms per liter (ppb)

source

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$ 444.17 New

performance standards (NSPS). Any new source subject to this subpart must achieve the following performance standards: Standards for TSS, arsenic, cadmium, chromium. copper, lead, mercury, silver, titanium, zinc and pH are the same as the corresponding limitation specified in $ 444.13.

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$ 444.18 Pretreatment standards for

new sources (PSNS). Except as provided in 40 CFR 403.7, any source that introduces wastewater pollutants into a POTW must comply with 40 CFR part 403 and achieve the following pretreatment standards: Standards for arsenic, cadmium, chromium, copper, lead, mercury, silver, titanium and zinc are the same as the

corresponding limitation specified in $144.16. [65 FR 4381, Jan. 27, 2000; 65 FR 33423, May 23, 2000]

PART 445—LANDFILLS POINT

SOURCE CATEGORY

Sec. 445.1 General applicability. 445.2 General definitions. 445.3 General pretreatment standards.

Subpart A-RCRA Subtitle C Hazardous

Waste Landfill

445.10 Applicability. 445.11 Effluent limitations attainable by the

application of the best practicable control technology currently available

(BPT). 445.12 Effluent limitations attainable by the

application of the best conventional pol

lutant control technology (BCT). 445.13 Effluent limitations representing the

degree of effluent reduction attainable by the application of the best available technology economically achievable

(BAT). 445.14 New source performance standards

(NSPS).

(b) The provisions of this part do not apply to wastewater discharges from land application or land treatment units, surface impoundments, underground injection wells, waste piles, salt dome formations, salt bed formations, underground mines or caves as these terms are defined in 40 CFR 257.2 and 260.10.

(c) The provisions of this part do not apply to wastewater generated off-site of a landfill facility, including wastewater generated off-site from washing vehicles or from waste transfer stations.

(d) The provisions of this part do not apply to discharges of contaminated ground water or wastewater from recovery pumping wells.

(e) This part does not apply to discharges of landfill wastewater from landfills operated in conjunction with other industrial or commercial operations when the landfill only receives wastes generated by the industrial or commercial operation directly associated with the landfill.

(f) This part does not apply to discharges of landfill wastewater from landfills operated in conjunction with other industrial or commercial operations when the landfill receives wastes generated by the industrial or commercial operation directly associated with the landfill and also receives other wastes provided the other wastes received for disposal are generated by a facility that is subject to the same provisions in 40 CFR subchapter N as the industrial or commercial operation or the other wastes received are of similar nature to the wastes generated by the industrial or commercial operation.

(g) This part does not apply to landfills operated in conjunction with Centralized Waste Treatment (CWT) facilities subject to 40 CFR Part 437 so long as the CWT facility commingles the landfill wastewater with other nonlandfill wastewater for discharge. A landfill directly associated with a CWT facility is subject to this part if the CWT facility discharges landfill wastewater separately from other CWT wastewater or commingles the wastewater from its landfill only with wastewater from other landfills.

(h) This part does not apply to landfills operated in conjunction with other

Subpart B-RCRA Subtitle D Non

Hazardous Waste Landfill

445.20 Applicability. 445.21 Effluent limitations attainable by the

application of best practicable control

technology currently available (BPT). 445.22 Effluent limitations attainable by the

best conventional pollutant control tech

nology (BCT). 445.23 Effluent limitations representing the

degree of effluent reduction attainable by the application of the best available technology economically achievable

(BAT). 445.24 New source performance standards

(NSPS). AUTHORITY: Secs. 301, 304, 306, 307, 308, 402 and 501 of the Clean Water Act, as amended (33 U.S.C. 1311, 1314, 1316, 1317, 1318, 1342 and 1361)

SOURCE: 65 FR 3048, Jan. 19, 2000, unless otherwise noted.

$ 445.1 General applicability.

(a) As defined more specifically in each subpart and except as provided in paragraphs (b) through (h) of this section, this part applies to discharges of wastewater from landfill units.

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