Standard Test Method for Estimating the Organic Fouling of Particulate Anion Exchange Resins

SCOPE
1.1 This test method provides a general estimate of the organic fouling of an anion exchange resin based upon total organic carbon measurements.
1.2 This standard does not purport to address all of the safety concerns, if any, associated with its use. It is the responsibility of the user of this standard to establish appropriate safety and health practices and determine the applicability of regulatory limitations prior to use. For a specific hazard statement, see Note 1.

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09-Dec-1998
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ASTM D5042-90(1998) - Standard Test Method for Estimating the Organic Fouling of Particulate Anion Exchange Resins
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NOTICE: This standard has either been superseded and replaced by a new version or withdrawn.
Contact ASTM International (www.astm.org) for the latest information
An American National Standard
Designation: D 5042 – 90 (Reapproved 1998)
Standard Test Method for
Estimating the Organic Fouling of Particulate Anion
Exchange Resins
This standard is issued under the fixed designation D 5042; the number immediately following the designation indicates the year of
original adoption or, in the case of revision, the year of last revision. A number in parentheses indicates the year of last reapproval. A
superscript epsilon (e) indicates an editorial change since the last revision or reapproval.
1. Scope 4. Summary of Test Method
1.1 This test method provides a general estimate of the 4.1 A sample of particulate anion exchange material is
organic fouling of an anion exchange resin based upon total contacted with a sodium chloride/sodium hydroxide solution at
organic carbon measurements. an elevated temperature. After a specified contact time, the
1.2 This standard does not purport to address all of the concentration of organic material in the aqueous phase is
safety concerns, if any, associated with its use. It is the measured as total organic carbon (TOC).
responsibility of the user of this standard to establish appro-
5. Significance and Use
priate safety and health practices and determine the applica-
5.1 One of the major factors in the unsatisfactory perfor-
bility of regulatory limitations prior to use. For a specific
hazard statement, see Note 1. mance of anion exchange resins is their fouling by organic
material. Knowledge of the degree of fouling can be used to
2. Referenced Documents
assess the condition of the resin and may indicate the need for
2.1 ASTM Standards: pretreatment of the influent, remedial cleaning procedures, or
D 1129 Terminology Relating to Water resin replacement.
D 1193 Specification for Reagent Water 5.2 It is recognized that this test method may not remove
D 2187 Test Methods for Physical and Chemical Properties and detect cation sloughage products or declumping agents. It
of Particulate Ion Exchange Resins is not intended to remove all organic compounds from the
D 2579 Test Methods for Total and Organic Carbon in resin.
Water 5.3 Since the chemical structures of organics compounds
D 2687 Practices for Sampling Particulate Ion-Exchange fouling the resin are generally unknown and are expressed only
Materials on the basis of their carbon content, interpretation of test
D 4839 Test Method for Total Carbon and Organic Carbon results to form a basis for predictions for resin performance or
in Water by Ultraviolet, or Persulfate Oxidation, or Both, cleaning procedures should be approached with caution.
and Infrared Detection 5.4 Samples may be taken before or after plant regeneration,
or both, depending on the type of information desired. This
3. Terminology
decision is left to the judgment of the user.
3.1 Definitions—For definitions of terms used in this test
6. Interferences
method, refer to Terminology D 1129.
3.2 Definitions of Terms Specific to This Standard: 6.1 The high sodium chloride (NaCl) concentration of the
3.2.1 organic fouling—buildup of organic material in or on test solutions may interfere with the response of the total
anion exchange resins by sorption during the service cycle and organic carbon analyzer. The response of the instrument should
incomplete removal during regeneration. be determined using standards prepared in this matrix.
This test method is under the jurisdiction of ASTM Committee D19 on Water
and is the direct responsibility of Subcommittee D19.08 on Membrane and Ion
Exchange Materials.
Current edition approved Mar. 30, 1990. Published October 1990. Fisher, S., and Otten, G., “Standardization of Methodology for Estimating the
Annual Book of ASTM Standards, Vol 11.01. Organic Fouling of Ion Exchange Resins,” Proceedings of the International Water
Annual Book of ASTM Standards, Vol 11.02. Conference, October 1989.
Copyright © ASTM International, 100 Barr Harbor Drive, PO Box C700, West Conshohocken, PA 19428-2959, United States.
D 5042 – 90 (1998)
7. Apparatus sodium hydroxide solution (see 8.3) to each. Cover the flask
with a small inverted beaker. Place flasks in a water bath at 90
7.1 Instrument to determine total organic carbon are as
6 2°C for 1 h.
specified in Test Methods D 2579, Oxidation—Infrared Detec-
10.3 After1hof heating, remove the flasks from the water
tion test method, or D 4839. TOC instruments using conduc-
bath. Add 50 mL of water and cool to room temperature. Filter
tivity detection have also been found to be suitable. The
the supernatant solution through a sintered glass funnel and
instrument must be capable of measuring CO formed without
neutralize to pH 3 to 5 by the dropwise addition of sulfuric acid
NaCl interference.
(see 8.4). Dilute to 100 mL in a volumetric flask. For some
8. Reagents TOC instruments, further dilutio
...

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