Bliley RJReynolds
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73519
2
EVALUATION OF PUBLIC HEALTH ASPECTS OF CARCINOGENIC/MUTAGENIC
BIOREFRACTORIES IN DRINKING WATER
PREV MED 9(2): 212-218; 1980
KRAYBILL, HF// WYNDER, EL~ SCHEEL, M, FRAUMENI~ J, HAMMOND~ EC;
HIGGINSON, J, SHUBIK' P; STELLMAN' S; WEISBURGER; JH, BULL,
BAILAR, JC
REVIEW:. AS PART OF ACONFERENCE ON PRIMARY PREVENTION OF CANCER
THAT DEALS WITH BOTH PREVENTIVE MEASURES AND THE RELATIVE IMPORTANCE
OF ENVIRONMENTAL RISK FACTORS, THIS ARTICLE EVALUATES THE PUBLIC
HEALTH ASPECTS OF CARCINOGENS AND MUTAGENS IN DRINKING WATER,
(16 REFS,)
DISCUSSION: "CARCINOGENS AND MUTAGENS HAVE BEEN IDENTIFIED IN
DRINKING WATER, DATA COLLECTED OVER THE PAST FEW YEARS HAVE
DEMONSTRATED THAT MATERIAL OBTAINED BY CONCENTRATING DRINKING WATER
WAS MUTAGENIC IN ~AND BALB 3T3 CELLS, MINIMALLY ~ONCENTRATED
DRINKING WATER SAMPLES (100- TO 200-FOLD) TREATED WITH DISINFECTANTS,,,
HAVE BEEN SHOWN TO PRODUCE MOUSE SKIN PAPILLOMAS IN TWO-STAGE
INITIATION PROMOTION STUDIES,,,, ADDITIVE EFFECTS OF CARCINOGENS
CANNOT BE OVERLOOKED AND THE FACT THAT SINGLE CHEMICAL ANALYSIS IN
RODENTS INDICATES CARCINOGENICITY RAISES SUSPICIONS THAT THE MULTIPLE
STRESS FROM CARCINOGENS IN WATER COULD CONTRIBUTE TO THE CANCER LOAD
IN MAN, HOWEVER, THE FACT THAT SOME CARCINOGENS FROM DRINKING WATER
MAY PERSIST IN BODY TISSUES MAKES QUANTIFICATION DIFFICULT, THE
EXPERIMENTAL INVESTIGATIONS THUS FAR PROVIDE ONLY PRESUMPTIVE
EVIDENCE AND THIS SITUATION MAY REMAIN UNTIL BETTER PROCEDURES ARE
DEVELOPED TO MEASURE THE TOTAL CARCINOGENIC INSULT OF MULTIPLE
COMPONENTS IN WATER BY ORAL ADMINISTRATION IN RODENTS OR FISH AS
ANIMAL MODELS,,,,
"WHILE THE CONCENTRATION OF A SINGLE CHEMICAL CARCINOGEN IN DRINKING
WATER WILL OCCUR AT MICROGRAM LEVELS, THE CONCENTRATION OF A COMPOSITE

73519
OF ALL CARCINOGENS HAS BEEN CALCULATED TO BE AT THE MILLIGRAM
LEVEL, A DOSE CAPABLE OR ACHIEVING A POSITIVE RESPONSE IN EITHER
ANIMAL MODELS OR IN MAN,,,,
"WHILE THESE EXPERIMENTAL AND EPIDEMIOLOGIC STUDIES PROVIDE SOME
SUGGESTIVE EVIDENCE ON THE POTENTIAL.HAZARD OF THESE CARCINOGENIC
BIOREFRACTORIES, ONE CANNOT DESCRIBE, WITH ASSURANCE~ ANY CAUSALITY
FOR CANCER BUT THE PROBABILITY REMAINS THAT THESE INGESTED WATER
CONTAMINANTS MAY CONTRIBUTE TO THE TOTAL CANCER BURDEN, WITH THIS
IN MIND IT SEEMS PRUDENT TO CONTROL AND/OR REDUCE THE EXPOSURE TO
CARCINOGENIC/MUTAGENIC CONTAMINANTS IN DRINKING WATER,"
/JP/
(PRESENTED AT AN AMERICAN HEALTH FOUNDATION/GERMAN CANCER CARE
CONFERENCE ON THE PRIMARY PREVENTION OF CANCER, NEW YORK~ NY~
JUNE 7-8, 1979,)
(PART OF A SERIES: SEE DOCUMENT Nos, 73510-73536,)
NAT CANC I~ BETHESDA, MD
REVIEW, CANCER PREVENTION, DRINKING WATER, WATER CARCINOGENS, WATER
MUTAGENS, WATER INGESTION, WATER SUPPLY, CANCER RISK FACTORS,
CHEMICAL CARCINOGENS, CHEMICAL MUTAGENS, WATER POLLUTION CARCINOGENICITY/
WATER POLLUTION HEALTH EFFECTS, GOVERNMENT ORGANIZATIONS,WATER
PURIFICATION, WATER CONTAMINATION, DISINFECTANTS, INDUSTRIAL CHEMICALS,
ORGANIC CHEMICALS, INORGANIC COMPOUNDS, INDUSTRIAL POLLUTION, NATURAL
CARCINOGENS, INDUSTRIAL CARCINOGENS, ENVIRONMENTAL CARCINOGENS,
CARCINOGENS CONTAMINATION, TRIHALOMETHANE CARCINOGENICITY, CHLORINE,
WATER ARSENIC~ WATER TRACE ELEMENTS, WATER MINERALS~ TRACE ELEMENTS
CARCINOGENICITY, SKIN CANCER, LIVER CANCER RISK FACTORS, LUNG CANCER
RISK FACTORS, LUNG CANCER TRACE ELEMENTS CAUSATION 1~ LUNG CANCER
ARSENIC CAUSATION 1, LUNG CANCER ARSENIC CAUSATION 2, ARSENIC
CARCINOGENICITY, ARSENIC INGESTION, METHodoLoGY ANALYSIS,
2

73519
METHODOLOGY VALIDITY, CARCINOGENS DETECTION, ENVIRONMENTAL EXPOSURE,
TUMOR PROMOTERS~ CANCER PROMOTERS~ CANCER INITIATORS~ PUBLIC HEALTH~
CARCINOGENS BIOASSAY~ NICKEL CARCINOGENICITY, WATER CHLORINATION~
LEAD INGESTION, LEAD CARCINOGENICITY~ WATER LEAD, EPIDEMIOLOGICAL
DATA EXTRAPOLATION~ BERYLLIUM CARCINOGENICITY~ LUNG CANCER
ENVIRONMENTAL FACTORS CAUSATION 1, ANIMAL EXPERIMENTS, RIVER WATER,
SURFACE WATER~ UNDERGROUND WATER, CANCER DRINKING WATER CAUSATION 1,
CANCER DRINKING WATER CAUSATION 2] CARCINOGENS POTENCY, GOVERNMENT
LEGISLATION~ GOVERNMENT REGULATIONS~ WATER POLLUTION LEGISLATION,
WATER POLLUTIONCONTROL, WATER COMPOSITION, DATA VALIDITY~ EXPERIMENTAL
METHODS VALIDITY~ ACTIVATED CHARCOAL, CANCER ENVIRONMENTAL FACTORS
CAUSATION 1, BLADDER CANCER RISK FACTORS, BLADDER CANCER ENVIRONMENTAL
FACTORS CAUSATION 1, CAUSAL VARIABLES, EPIDEMIOLOGICAL STUDY
VALIDITY, EPIDEMIOLOGICAL METHODS, POPULATION SAMp~E. VALIDI.TY, ..........
POPULATION MOBILITY~ POPULATION STRUCTURE CHANGES~.HEALTH STATISTICS~
INTERPRETATION VALIDITY~ POPULATION SAMPLE SIZE VALIDITY, STATISTICAL
ASSOC, EXPERIMENTAL ACCURACY, EPIDEMIOLOGICAL STUDY HI, ADDITIVE
EFFECTS, MULTIPLE FACTORS INTERACTION, DNA BINDING~ CARCINOGENS
BINDING, ORGAN SUSCEPTIBILITY, TISSUE SUSCEPTIBILITY, CARCINOGENS
SUSCEPTIBILITY~ RISK ESTIMATION, MATHEMATICAL MODEL~ SPECIES
DIFFERENCES A~ SPECIES DIFFERENCES, SPECIES SUSCEPTIBILITY
SPECIES SUSCEPTIBILITY, SPECIES SPECIFICITY A, SPECIEs SPECIFICITY,
CARCINOGENS SPECIFICITY, SYNERGISM, CARCINOGENS INGESTION, ANIMAL
MODEL EXTRAPOLATION~ CARCINOGENS DOSE, FISH/
VIRUS CONTAMINATIDN~ BACTERIAL CONTAMINATION, PARASITES~ WATER
FILTRATION, CHLOROFORM CARCINOGENICITY~ WATER NITRITE, NITRITE
CARCINOGENICITY~ DIGESTIVE CANCER RISK FACTORS, GAS LIQUID
CHROMATOGRAPHY~ MASS SPECTROMETRY, ANALYTICAL METHODS~ WATER
CHEMICAL ANALYSIS~ THRESHOLD VALUE, DNA REPAIR~ CELL CULTURE
TECHNIQUES A, BACTERIA~ CELL TRANSFORMATIONS MALIGNANT
TRANSFORMATION, CIGARETTE SMOKING, BLADDER CANCER SMOKING CAUSATION 1~
CORRELATION COEFFICIENTS~ REGRESSION COEFFICIENTS, MICE~ 0ZONE~
SKIN TUMOR A, SKIN PAPILLOMA A~ CARCINOGENS DOSE A~.DRINKING
WATER A~ WATER CARCINOGENICITY A, CHEMICAL REACTION, CHEMICAL
REACTIVITY, CARCINOGENS BIOASSAY A, CARCINOGENS DETECTION A,
3

73519
1 1 1 TRICHLOROETHANE~ POLYCYCLIC AROMATIC HYDROCARBONS CARCINOGENICITYj
CARCINOGENS ADMINISTRATION ROUTE A, BLADDER CANCER OCCUPATIONAL
FACTORS CAUSATION 1~ BLADDER CANCER ALCOHOL CAUSATION 1, BLADDER
CANCER DRUGS CAUSATION 1] BLADDER CANCER COFFEE CAUSATION 1, BLADDER
CANCER ETHNIC FACTORS CAUSATION 1, BLADDER CANCER SOCIOECONOMIC
FACTORS CAUSATION 2,BLADDER CANCER DIETARY FACTORS CAUSATION 1,
COFFEE INeESTION, ALCOHOL INGESTION, DRUG INGESTION, WATER
BENZO A PYRENE, WATER POLYCYCLIC HYDROCARBONS~. BENZO.A PYRENE
CARCINOGENICITY, POLYCYCLIC HYDROCARBONS CARCINOGENICITY)CARBON
TETRACHLORIDE CARCINOGENICITY, VINYL CHLORIDE CARCINOGENICITY~
DIOXANE, METHYL IODIDE, DDT, CHLORDANE~ LINDANE, DIELDRIN,
BENZENE CARCINOGENICITY, VINYLIDENE CHLORIDE, TRICHLoROETHYLENE
CARCINOGENICITY, TETRACHLOROETHYLENE, HEPTACHLOR EPOXIDE,
~IETHYL BROMIDE, !~ETHYL CHLORIDE, ALDRIN CARCINOGENICITY,
0CTADECANE, TETRADECANE, PESTICIDES CARCINO~ENICITY~ ~ETHYLENE
CHLORIDE, 1 2 DICHLOROPROPANE, DICHLOROETHANE~ ACRYLONITRILE ..
CARCINOGENICITY~ 1 3 BUTADIENE~ PYRENE CARCINOGENICITY, 0 CRESOL,
2 q DIMETHYLPHENOL, PHENOL CARCINOGENICITY, DODECANE,
DECANE, LIMONENE/
ENGLISH LANGUAGE, BETHESDA MD RESIDENCE~ USA RESIDENCE, CONFERENCE~
GRANTOR AMER HEALTH FOUND, GRANTOR GERMANY CANCER CARE~ NEW YORK
ARGENTINA, USA USPHS NATL CANCER INST, US NATL ACAD ScI, NEW YORK
ACAD SCI~ MISSISSIPPI RIVER, AMER CANCER SOC, INTERNATL AGENCY
RES CANCER, US ENVIRONMENTAL PROTECTION AG£NCY~ TAIWAN~" EPPLEY INST
RES CANCER
4

PREVENTIVE MEDICINE 9, 163- 164 (1980)
Conference on the Primary Prevention of Cancer:
Assessment of Risk Factors and Future Directionst
American Health Foundation, 320 East 43rd Street,
New York, New York 10017, June 7-8, 1979
Forward Ernst L. Wynder
Introduction Mildred Scheel
Assessment of Risk Factors
Panel 1, Chairman: Johannes Clemmesen
Tobacco E. Cuyler Hammond and Herbert E.
Seidman
Alcohol Kenneth J. Rothman
Occupations John Higginson
Panel 2, Chairman: Charles B. Arnold
Nutrition
Food Additives
Drugs
Anthony B. Miller
Philippe Shubik
Paul D. Stolley
Panel 3, Chairman: John C. Bailar
Air Pollution
Water Pollution
Radiation
Ultraviolet Light
E. Cuyler Hammond and
Lawrence Garfinkel
Herman F. Kraybill
Seymour Jablon, John C. Bailar, and
Arthur C. Upton
Frederick Urbach
Panel 4, Chairman: Gregory T. O'Conor
Genetics Henry T. Lynch
Virology Fred Rapp
Immunology Alexandra H. Filipovich, Beatrice I).
Spector, and John Kersey
Assessment td' Risk Factors for Cancer
Legislative Medicine
European Viewpoint
U.S. Viewpoint
Heahh Education
Chairman: Walter G. James
Peter Greenwald
Dietrich Schmahl
Albert C. Kolbye, Jr.
Sponsored by the American Health Foundation, Dr. E. L. Wynder, President; and the Deutsche
Krebshilfe, Bonn, F.I).R.. Dr. Mildred Scheel. President.
163
0091-7435/80/020163-02502.00/0
Copyright (~ 1980 by Academic Press, Inc.
All rights of reproduclion in any form reserved.

164
Health Education for Children
Health Education for Adults
Product Mod~/~cation
Chairman: Harry Demopoulos
The Less Harmful Cigarette
CONFERENCE~ PRIMARY PREVENTION OF CANCER
Christine L. Williams
Walter G..lames
Extending the Prudent Diet
Priorities in Cam'er Prevention: A
Conference Al~praisal
Future Directions in Cancer Prevention
Future Directions in Cancer Prevention
The Deutsche Krebshilfe:
A Catalytic Mode of Action
Future Directions of Primary Cancer
Prevention in the Federal Republic of
Germany
Cancer Research Programs of the
American Cancer Society
Dietrich Hoffmann, T. C. Tso, and
Gio B. Gori
John H. Weisburger, D.Mark
Hegsted, Gio B. Gori, and
Barry Lewis
Gio B. Gori
Arthur C. Upton
P. H. Hofschneider
Georges Fulgraff
LaSalle D. Leffall, Jr.

PXEVI~NI IVI~ MIiDICiNF. 9, 212-218 {1980)
Evaluation of Public Health Aspects of
Carcinogenic/Mutagenic Biorefractories in Drinking Water1
HERMAN F. KRAYBII.L
N.lio#tol ('¢t~tcer II~.~litttlc
Room 3C37, La#tdo.' B.ihlin,~. I'h'the.~'da, Moryhtltd 211205
COMMITTEE MEMBERS
E. CI~Yt I.r IIAMMONI),
JIHIN HI(;(;INSON, M.D.
htl('rottfiotlal A.t, ettc)'.Ji~r Re.search
World Health
PIIII IPPE StlUBIK. M.D.
IQ~ph,y In.~titttte,lbr Research in Cancer,
Utdrersit.v o.]" Nebraska Medical Center
SlE'¢EN SIf:l 1 MAN.
American Ih'alth
JollN H. WI!iSIIt~R(;I!R. PIt.D.
American th, alth t'ottndaliott
AI the turn of the century, concern over conl:lmination of drinking water was focused on
that caused by viruses, bacteria, and parasites. However, in the developed countries allen-
lion is currenlly focused on organic chemical contaminants and, to a lesser exlent, the
inorganic chemicals. Of the wide spectrum of organic biorefractories in potable water, an
identification and classification of a list of 309 in 1977 revealed 23 carcinogens and 30
mutagens. A current list updating such information may reveal a larger number, While some
chemicals in drinking waler, such as arsenic and nitrite, were incriminated in studies some
years ago with regard to cancer, current studies on organic biorefractories are inconclnsiv¢.
Some experimental studies in systems, in ritro and in fifo. would indicate some mulagenic
and carcim'~genic aclivity, however, more comprehensive sludies are needed to provide
more convincing evidence on cause and effecl. Similarly. there have been 12 reported
epidemiological studies of various types, some of which suggest interesting statistical as-
sociations. The studies, however, are limited with some uncontrolled variants, Future
studies will have to correct for certain deficiencies. While the experimental and
epidemiologic studies provide some presumptive evidence, one cannot establish, with any
degree of asst.rance as yet, any causality relevant to cancer from these micropollutants.
There is serious concern, however, about those contaminants with the realization that the
ingested curcinogenic-mutugeni¢ biorefractories may contribute to the total cancer burden.
Thus, control and reduction technologies in water treatment are recommended.
INTRODUCTION
According to the U.S. Environmental Protection Agency (EPA) there are
40,000 municipal water systems providing drinking water, as well as 200.000 water
supply systems for nonresidential locations (15). Many of these systems are not
equipped to treat water from contaminated sources but are designed to disinfect
' Presented at th'e American Health Foundation/I)culsche Krebshilfe Conference on the Primary
Prevention of C,'mcer: Assessmenl of Risk Factors and Future Directions. N.Y., N.Y.. June 7-8, 1979.
212
0091-7435/80/020212-07502.1)0/0
Copyr~h! ~ |gHo by Academic Prc~, Inc.
All ri|hts of reproduction in any form reserved.

CONFERENCE: PRIMARY PREVENTION OF CANCER
213
relatively pure water from selected sources. At the turn of the century most
concern was centered upon processes which removed viruses, bacteria, and cer-
lain parasites. Sedimentation filtration and disinfection have virtually eliminated
these potential disease vectors. However, inorganic and organic chemicals have
appeared as new contaminants as a result of industrial activities and, to a lesser
extent, as recognizable contaminants in natural water supplies. Some of the or-
ganic contaminants such as the trihalomethanes (chlor.oform, bromoform, di-
bromochloromethane, dichlorobromomethane) are the result of attempts to reduce
bacterial contamination by using the disinfectant chlorine. Most attention is fo-
cused on the more significant qualitative and quantitative aspects of organics over
the inorganics.
More studies need to be conducted on inorganic contaminants in water. In a
study conducted on nitrite in drinking water, there appeared to be an association
between levels of nitrite and incidence of gastric cancer. Levels of nitrite in
drinking water were 80 ppm (4). Arsenic in drinking water in Taiwan and Argen-
tina was associated with cancers of the skin, lung, liver, and other organs (6, 16).
While these inorganic elements could be the etiologic agents, it is conceivable that
on the basis of current sophisticated analytical methodology (gas-liquid chroma-
tography and mass spectrometry), other contaminants might have been identified
as the primary water contaminants in these statistically associated cancers.
It is possible to estimate the levels of some volatile organic chemicals in water
but the nonvolatile organics are much harder to identify and it is estimated that
one can only account for 10% of the total organic chemicals (TOC) present as
biorefractories in drinking water. Thus, if the larger component includes some
carcinogenic organics, the total levels of carcinogenic contaminants could be un-
derestimated. The EPA monitoring systems now have identified 699 biorefrac-
tories in the USA water supplies. Of an original list of 309 biorefractories in 1977,
the National Cancer Institute (NCI) has identified and classified 23 carcinogens,
30 mutagens, and il promoters in drinking water (9) (Tables 1-3). This list is
currently being updated.
An excellent report entitled "Safe Drinking Water," prepared by the National
Academy of Sciences (NAS) in 1977 at the request of the EPA, considers the
public health aspects of viruses, solid particles, inorganic solutes, pesticides,
radioactivity, and the major component of interest, the organic biorefractories (12).
The report is quite detailed on safety and risk assessment and includes most of the
current issues on carcinogenesis such as animal-to-man extrapolations, thresh-
olds, dose-response, repair mechanisms, and potential interaction of chemicals.
A conference on Biological Effects of Aquatic Pollutants with Emphasis on
Neoplasia was held by the New York Academy of Sciences in 1976 (14).
ASSESSMENT OF THE PROBLEM
As early as 1950, the National Cancer Institute studied the carcinogenicity of
water pollutants (?). These studies employed bioassays on industrially polluted
water as did some later studies (5). These studies, despite the crudity of experi-
• mental approaches, showed some suggestive evidence but the findings were not
too convincing. Other NCI epidemiologic studies followed in an attempt to relate
inorganic materials in river basins to cancer mortality. They raised some suspi-
cions about nickel, arsenic, beryllium, and lead (1).

214
HERMAN F. KRAYBIi.I.
TABLE I
CARCINO(IENS ANI) ~USI'I'.('I |il) CAR('INO(IENS IN DRINKIN(I WA I~ER (U.S.A.)
I. Benzolu)pyrene
2. Carbon telrachloride
3. Chloroform
4. Vinyl chloride
5. 1,4-Dioxane
6. Methyl iodide
7. DI)E
8. DDT
9. Chlordane
I0. Lindane
II. Dieldrin
12. Benzene
13. Vinylidene chloride
14. fleplachlor
15. I, 1,2-Trichloroethane
16. I, 1,2-Trichloroelhylene"
17. l~i~( 2-chhu'oelhyl)ether
18. Simazine
19, Telraehloroelhylene
20. Heplachlor epoxide
23. Bulyl bromide
" Recent reports attribute NCI reported carcinogenicily of TCE to epichlorhydrin as stabilizer
addi-
tive in technical grade TCE and not to pure TCE.
As indicated, a spectrum of the organic chemicals identified in drinking water
has been shown to be carcinogenic in bioassays (Table I). There is some evidence
that marine animals in polluted waters show a fourfold increase in tumor incidence
compared with those from less-polluted waters (2).
There are two approaches to assessment of the carcinogenic hazard of drinking
water contaminants. The first would be toxicity studies or carcinogenic bioassays
on a mixture or composite of these micropollutants in water using various experi-
mental systems such as whole animal bioassays on concentrates of drinking water
samples, synthetic formulation of water samples with identified contaminants at
determined levels added to relatively uncontaminated water, bioassay of water
samples using the fish as the animal model, and bioassay of water samples on cell
cultures and bacterial systems (Ames' procedure) for determination of
mutagenicity and cell transformations. The second approach entails epidemiologic
and statistical studies on various human populations. Some of these studies relate
to investigation of relationships between the levels of trihalomethanes in water
and possible increases in cancer. Other studies have focused on effects of chlori-
nation on surface waters versus ground water, probably not chlorinated, in terms
of comparative incidences and possible increases in human cancer.
SYNOPSIS OF STUDIES CONDUCTED
Some preliminary reports from experimental i, vitro studies indicate that con-
centrates of municipal water supplies and fractions of these concentrates have
mutagenic and carcinogenic activities (i I). The EPA, however, has proposed

CONFERENCE: PRIMARY PREVENTION OF CANCER
'I'A I~II.E 2
Mut A(iliNS ANI) SUSI'I ('II.I) MtilA(il NS IN I)RINKIN(; WA l liR
I. I,l,I-Trichlt~roclhanc
2. I|romtm~¢llu~i~c (methyl hronlidcl
3. Methyl cldoride
4. Bromochloromclhane "
5. Methylene chloride
6. Bromtfform
7. Brtm~odichloromet bane
8. 2-Chltlropropane
9. 1,2-1)ichloropropane
Ill. I-Chloropropcne
I1. 1,2-1)ichlorocthane
12. Bis(2-¢hloroisopropyl)et her
13. Chlorodibromomelhane
14. 1,3-1)ichloropropcne
15. 2.6-1)initroloh~cnc
16. I)i¢ hloroa¢clonilrile
17. Melhylcne bromide
18. Chlordane
19. Vinylidcne chloride
21L n-Btltylbromidc
21. Bisl2-chloroct hyl)cther
215
24. Methyl iodide
25. Vinyl chloride
26. 1,3-Butadicne
27. 1,2-Bistchloroethyoxy~ethane
28. Pyrene
29. I, 1.2-Trichloroe~hylene
.t0. Tetrachloroethylene (perchloroethylene)
various approaches, augmented by those of the NCI previously mentioned, to
determine the carcinogenic potency, if any, of contaminated drinking water in
order to establish whether low concentrations of these organic trihalomethanes at
the proposed regulation of 100 ppb ( 100 ~g/liter) really afford a measure of safety.
TABLE 3
PROMOIER~i IN DRINKING WAIER (U.S.A.)
I. Ortho-cresol
2. 204-Dimethylphenol
3. Phenol
4. n-Dod¢cane
5. Eicosane
6. 2,4-Dichlorophenol
7. n-I)¢cane
8. Limonene
9. Octadec.',ne
10. n-Telradecan¢
II. n-Unde~ane
