Analytical Development Work for Detergent ABS Determination in Waste Waters
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Transcript of Analytical Development Work for Detergent ABS Determination in Waste Waters
Analytical Development Work for Detergent ABS Determination in Waste WatersAuthor(s): Ralph HouseSource: Sewage and Industrial Wastes, Vol. 29, No. 11 (Nov., 1957), pp. 1225-1227Published by: Water Environment FederationStable URL: http://www.jstor.org/stable/25033469 .
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ANALYTICAL DEVELOPMENT WORK FOR DETER GENT ABS DETERMINATION IN WASTE WATERS
By Ralph House
Chairman, Subcommittee for Analysis of ABS, Association of American Soap and Glycerine Producers
Formation of Analytical Committee
In 1954 the Technical Advisory Committee of the Association of Amer ican Soap and Glycerine Producers
(AASGP) formed an analytical sub committee to develop improved analyti cal procedures for detergent alkyl benzene sulfonate (ABS) in sewage and receiving waters. Representatives from several interested organizations have been associated with the work of this committee. Those organizations
which have been represented on the committee are : Atlantic Refining, Cali fornia Research Corporation, Colgate Palmolive, Continental Oil, Lever Bro
thers, Monsanto Chemical, National
Aniline, Procter and Gamble, and the U. S. Public Health Service.
Need for Improved Analytical Methods
Interest in improved analytical pro cedures for ABS arose because of com
plaints that detergents caused operat ing difficulties in sewage treatment
works and might be undesirable con taminants in surface waters. ABS is the principal active ingredient in most household detergents. These products ordinarily contain 15 to 30 per cent active ingredient, the remainder being primarily inorganic builders.
Use concentration of household de
tergents varies from about 0.1 to 0.3
per cent (1,000 to 3,000 p.p.m.) in the wash water. High dilution in the sew ers with detergent-free water gives very low concentrations at the sewage treat
ment plant. Still further dilution oc curs in receiving waters. At these low
concentrations, natural organic matter
present in sewage and surface waters
might be expected to interfere with direct colorimetric methods.
Interferences in Colorimetric Methods
The basic method for estimating ABS in trace concentrations is that of Jones (1). In this method a cationic
dye (m?thyl?ne blue) is reacted with the anionic sulfonate to form an oil soluble compound which is extracted into chloroform and measured colori
metrically. Colorimetric methods of this type
work quite well in distilled water, but serious interferences are sometimes
present in sewage and surface waters. Numerous attempts to eliminate or cor rect for interferences have been made.
Degens et al. (2) found that inter ference from nitrate and thiocyanate ions can be minimized. Edwards and
Ginn (3) titrated with a quaternary ammonium compound at pH 7.0 to 7.5 to eliminate interferences from soaps and proteins which occur in alkaline and acid solutions, respectively. This titration method is primarily of inter est at concentrations of 100 p.p.m. and
higher, and is only of limited use at the much lower concentrations to be
expected in sewage and surface waters.
Longwell and Maniece (4) eliminated
protein and soap interference by first
extracting at pH 10 and then washing with acidified m?thyl?ne blue. Moore and Kolbeson (5) used methyl green instead of m?thyl?ne blue and extracted
with benzene instead of chloroform. The nature of interferences was altered
1225
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1226 SEWAGE AND INDUSTRIAL WASTES November, 1957
by the changes, but the interferences were not eliminated.
Unfortunately proof that the effects of interferences have been eliminated can only be obtained by comparison
with results from a method of known
high accuracy or by recovery and iden tification of the ABS. In the absence of such a method, there was consider able doubt that reported results based on colorimetric methods were accurate.
Interferences from proteins and soluble
inorganic compounds can probably be
eliminated, but some naturally occur
ring organic sulfates and sulfonates
may still interfere. Positive interferences have been re
ported by Fairing and Short (6) using the direct m?thyl?ne blue procedure on
urine and aqueous extracts of straw,
manure, leaves, and rotted wood.
Hooker and others (7) found similar
positive interference in urine and
aqueous extracts of coffee, tea, straw,
and paper mill wastes using various
modifications of Jones7 method such as
those of Longwell and Maniece (4) and
Degens et al. (2). Many of the complaints about ABS
as a pollutant are based on the above
types of analytical procedures. Others are based on the appearance of froth,
which is not as reliable an indication
of the presence of detergents as is com
monly supposed. The type of froth ob
tained with ABS at a few parts per million is quite unstable and disap
pears rapidly. On the other hand,
many proteinaceous materials and
other natural products such as bile
salts are surface active and can pro
duce stable froths under some condi
tions. In light of these considerations, it is evident that less equivocal analyti cal data are needed to clarify the sit
uation.
Status of Committee Work
Referee Method for Water
Two requisites of a referee method
are: (a) complete (or reproducible) re
covery of ABS and (b) positive identi fication of the recovered material. Colorimetric methods cannot fulfill these requirements. The committee therefore agreed that its first objective
would be to develop a method to re cover ABS as quantitatively as possible from very dilute solutions, then to
purify the recovered ABS sufficiently for positive identification.
Under the chairmanship of P. J.
Weaver, Procter and Gamble Company, a referee method for ABS in water was
developed after considerable work in the laboratories of the various member
organizations. This method and the re
sults of cooperative testing of Ohio River water were presented before the American Chemical Society Summer
Symposium on Analytical Chemistry at the University of California, Los An
geles, Calif., on June 14, 1956, by a
member of the committee (8). Essen
tially 100 per cent of the ABS is de
tected using this method. The method involves adsorption of
the ABS on activated carbon, elution,
purification by acid hydrolysis and ex
tractive techniques, and final estima tion and identification by infrared spec
troscopy. The procedure is lengthy and not suited for survey work. How
ever, it satisfies the original need of a
referee method for resolving controver
sial cases and for establishing the valid
ity of shorter methods.
Referee Method for Sewage
The committee is currently investi
gating a similar method for use in sew
age. Results to date on local sewage
samples are encouraging, and it is ex
pected that cooperative tests will be
carried out on a sewage sample in the
near future. If this procedure proves
satisfactory, it will be made generally available.
Short Method
A short method for determining ABS
in sewage and surface waters is needed
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Vol. 29, No. 11 DETERGENT RESEARCH 1227
so that reliable data can be obtained in the field by sewage plant personnel and others interested in ABS concen tration levels. The committee decided that a project to develop such a method could best be carried out by an inde
pendent research organization to speed results and avoid undue work load on
committee member organizations. A number of universities and re
search institutes were contacted, and several who were interested in the prob lem submitted proposals for the proj ect. On the basis of previous experi ence and interest in similar analytical problems in the field of pharmacology, the proposal of Professor Orville H.
Miller and V. J. Patel of the University of Southern California School of Phar
macy was accepted. Work on the proj ect started in July, 1957.
When a successful short method has been developed, it is hoped that a large amount of reliable data on the ABS content of sewage and receiving wa
ters throughout the country can be ac
cumulated. When sufficient data are
available, it should be possible to clar
ify the situation regarding ABS as a
potential trouble maker in sewage
plants and water pollution.
References
1. Jones, J. H., "
General Colorimetric Method for Determination of Small
Quantities of Sulfonated or Sulfated Surface Active Compounds.'9 Assoc.
Official Agr. Chemists, 28, 398 (1945). 2. Degens, P. N., Evans, H. C, Kommer, J.
D., and Winsor, P. A., "
Determina tion of Sulphate and Sulphonate
Anion-Active Detergents in Sewage.'' Jour. Appl. Chem., 3, 2, 54 (Feb., 1953).
3. Edwards, G. P., and Ginn, M. E., "De termination of Synthetic Detergents in
Sewage." This Journal, 26, 8, 945
(Aug., 1954). 4. Longwell, J., and Manieee, W. D.,
" De
termination of Anionic Detergents in
Sewage, Sewage Effluents and River Waters." Analyst, 80, 167 (Mar., 1955).
5. Moore, W. A., and Kolbeson, R. A., "De termination of Anionic Detergents in
Surface Waters and Sewage with
Methyl Green." Anal Chem., 28, 2, 161 (Feb., 1956).
6. Fairing, J. D., and Short, F. R., "Spee trophotometric Determination of Al
ky lbenzenesulfonate Detergents in Surface Water and Sewage." Anal.
Chem., 28, 12, 1827 (Dec, 1956). 7. Hooker, D. T., Sallee, E. M., and Weaver,
P. J., Unpublished data, Procter and Gamble Co. (1955).
8. Sallee, E. M., et al., "Determination of Trace Amounts of Alkylbenzenesulfo nates in Water." Anal. Chem., 28, 12, 1822 (Dec, 1956).
MEMBERSHIP DIRECTORY
The biennial complete directory of Federation membership for the 1957 calendar year will be a featured part of the March, 1958, issue of This Journal.
Be certain that your listing is up-to-date. Turn to page 1251 of this issue for full information.
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