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CAS ONLINE@
The CA file contains records for the documents covered in Chemical Abstracts for
the time period 1967-present. Chemical Abstracts covers journals, patents,
technical reports, books, conference proceedings, and dissertations from all
areas of chemistry and chemical engineering, worldwide. The CA file contains
over 6 million records, and is updated biweekly with an additional 14,000-18,000
citations.
The document records in this file contain bibliographic and indexing information
for searching. Over 60% of the records also contain abstracts for display. The
next two pages of this pamphlet give information on the search and display
fields in the CA file, the formats which are available for online DISPLAY and
offline PRINT of records, and show samples of journal and patent records.

ANSWER 1
AN CA103(5):33308e
TI Decomposition reactions of (hydroxyalkyl)nitrosoureas and related
compounds: possible relationship to carcinogenicity
AU Singer, Sandra S.
CS Frederick Cancer Res. Facil., NCI
LO Frederick, MD 21701, USA
SO J. Med. Chem., 28(6), 1088-93
SC 4-6 (Toxicology)
DT J
CO JMCMAR
IS 0022-2623
F'Y 1985
LA Eng
AB Decompn. reactions of the title compds.,
1-(2-hydro:<yethyl)-1-nitrosourea C13743-07-2],
1-(2-hydroxypropyl)-1-nitrosourea C71752-69-7],
3-nitrosooxazolid-2-one C38347-74-97, and
5-methyl-3-nitrosooxazolid-2-one C79624-33-2], were studied in aq.
buffers at physiol. pH to det. the pattern of product formation that
might be related to carcinogenesis. Related dialkylnitrosoureas were
also subjected to decompns. in buffer followed by product anal. The
products predicted by literature mechanisms for these decompns. were
the compds. formed. The tests compds. were dissolved at pH 6.4-7.4
in 0.067 or 0.1M phosphate buffer at 37.degree. employing several
methods of anal. At the above pH, epoxides were stable reaction
products; however, in the presence of hepatocytes, most epoxides were
converted to glycols. The results reveal no clear-cut pattern of
product formation that could be directly related to carcinogenesis.
Some of the products were highly active compds. which are carcinogens
in their own right, and they may be responsible for some or all of
the carcinogenic activity ofthe test compds. if they are formed by
decompn. of the test compds. at the target organ.
KW carcinogenicity alkylhydroxyurea nitrosooxazolidone decompn
IT Degradation
(of (hydroxyalkyl)nitrosoureas and related compds.,
carcinogenicity in relation to)
IT 75-07-0, biological studies 75-21-8, biological studies 107-21-1,
biological studies
(as (hydroxyethyl)nitrosourea decompn. product, carcinogenicity in
relation to)
IT 57-55-6, biological studies 67-64-1, biological studies 75-56-9,
biological studies 123--38-6, biological studies
(as (hydroxypropyl)nitrosourea decompn. product, carcinogenicity
in relation to)
IT 107-07-3, biological studies
(as chloroethylurea deriv. decompn. product, carcinogenicity in
relation to)
IT 7086-00-2 57178-82-2
(as deuterohydroxyethylurea deriv. decompn. product,
carcinogenicity in relation to)
[7C7 VJC7280
1.

IT 1U8-32-7
(as methylnitrosooxazolidone decompn. product, carcinogenicity in
relation to)
IT 96-49-1
(as nitrosooxazolidone decompn. product, carcinogenicity in
IT relation to)
154-93-8 13010-47-4 13743-07-2 38347-74-9
59960-30-4
6U784-46-5 66929-45-1 71752-69-7 75014-24-3 77081-3o-2
79624-33-2 96806-34-7 96806-35-8
(decompn. of, carcinogenicity in relation to)

ANSWER 2
AN CA103(3):18258v
TI An evaluation of the utility of four in vitro short term tests for
predicting the cytotoxicity of individual compounds derived from
tobacco smoke
AU Curvall, Margareta; Enzell, Curt R.; Pettersson, Bertil
CS Res. Dep., Swed. Tobacco Co.
LO Stockholm S-104 62, Swed.
SO Cell Biol. Toxicol., 1(1), 173-93
SC 4-B (Toxicology)
DT J
CO CBTOE2
IS 0742-2091
F'Y 1984
LA Eng
AB Biol. activity of 305 compds. (12 groups according to main
functionality) was compared by 4 in vitro tests, i.e., the cell
growth of Ascites sarcoma BF 8 cells, the oxidative metab. of
isolated brown fat cells from adult hamsters, the membrane damage of
human diploid embryonic lung fibroblasts, and the ciliary activity of
embryo chicken trachea. The results are tabulated. The phenols
constitute the most active group, followed by aldehydes and alcs.
The least active are the furans/thiophenes and the esters. Among the
phenols, the alkylphenols are highly active. To find whether the
toxicity of some of these compds. belonging to different groups might
be due primarily to a common subunit, 45 descriptors were selected
which included the 12 functionalities. The computer-assisted
matching of these and any combination of them against the mean
activity showed the most toxic single descriptor group to be
terpenoids followed by indoles and naphthalenes; the most toxic
2-descriptor group was .alpha.,.beta.-unsatd. carbonyls, followed by
n-alkyl alcs., aldehydes, and acids. Intersystem similarities and
differences, using a high-medium-low scale, indicated that all the 4
test systems give the same results for 35% of the compds.
KW chem cytotoxicity prediction; tobacco smoke chem cytotoxicity
IT Trachea
(ciliary activity of, cytotoxicity prediction for chem. compds. of
tobacco smoke from in vitro tests in relation to)
IT Tobacco smoke and smoking
(components of, toxicity of, cytotoxicity prediction from in vitro
tests in relation to)
IT Molecular structure-biological activity relationship
(of compds. o+ tobacco smoke, cytotoxicity prediction from in
vitro tests in relation to)
IT Cell membrane
(of lung fibroblast, cytotoxicity prediction for chem. compds. of
tobacco smoke from in vitro tests in relation to) OD
IT Anhydrides Go
Alcohols, biological studies ~
Aldehydes, biological studies (~
Amines, biological studies (~
Aromatic hydrocarbons, biological studies N
Carboxylic acids, biological studies OD
Esters, biological studies N

Ethers, biological studies
1':etones, biological studies
Phenols, biological studies
Terpenes and Terpenoids, biological studies
(toxicity of, of tobacco smoke, cytotoxicity prediction from in
vitro tests in relation to)
IT Sarcoma
(ascites, cell growth inhibition of, cytotoxicity prediction for
chem. compds. of tobacco smoke from in vitro test in relation to)
IT Adipose tissue, metabolism
(brown, adipocyte, oxidative metab. by, cytotoxocity prediction
for chem. compds. of tobacco smoke from in vitro tests in relation
to)
IT Toxicity
(cyto-, of chem. compds. of tobacco smoke, prediction of, in vitro
tests in relation to)
IT Heterocyclic compounds
(nitrogen, toxicity of, of tobacco smoke, cytotoxicity prediction
from in vitro tests in relation to)
IT
100-83-4
1 i~3-69-5
104-93-8 10~~-84-5
103-73-1
105-53-3 101-81-5
1~~4-53-0
105-67-9
biological studies 106-44-5,
biological studies 107-02-8,
107-12-0 107-1.T--1, biological
biological studies 108-=8-3,
biological studies 108-44-1,
biological studies 108-48-5
~ studies 108-68-9 108-75-8
studies
85-01-8,
87-51-4,
89-81-6
90-15-3
studies
95-13-6
studies
50-32-8, biological
biological studies
biological studies
biological studies
bioloc}ical studies
67-63-0, biological
biological studies
78-84-2 78-85-3
80-56-8
biological
biological
90-00-6
91-10-1
91-55-4
95-20-5
studies 51-17-2 54-11-5
59-67-6, biological studies
64-17-5, biological studies
64-19-7, biological studies
66-25-1 67-47-0 67-56-1,
studies 67-64-1, biological
75-05-8, biological studies
78-9.3-3, biological studies
83-32-9 83-33-0 83-34-1
studies 85-44-9 86-28-2
studies 87-59-2 87-62-7
90-02-8, biological studies
91-20-3, biological studies
91-57-6 91-59-8 91-64-5
95-48-7, biological studies
95-65-8 95-78-3 95-87-4 96-17-3
98-00-0 98-82-8 98-86-2, biological studies
56-55-3 57-55-6,
60-12-8 62-53-3,
64-18-6,
65-85-0,
biological studies
studies 71-43-2,
78-81-9
78-94-4,
84-66-2
B6-53-3
87--66-1
90-05-1
91--_-5,
93-04-9
95-5.3-4 ,
97-51-0
98-92-0
78-82-0
biological
84-74-2
86-74-8
83-05-1
90-12-0
biological
93-18-5
biological
97-54-1
99-49-0
99-93-4 100-21-0, biological studies 100-41-4, bioloqical studies
100-42-5, biological studies 100-46-9, biological studies
100-47-0, biological studies 100-51-6, biological studies 100-52-
7, biological studies 10t:)-,°,4-9 100-66-3, bioloQical studies
101-84-8 103-41--' 10.=-65-1 ~
104-55-2 104-85-8 1+'!4-97-i i
106-21-B 106-24-1 106-42-.?, M
biological studies 106-49-c_,
biological studies 107-11-9
studies 107-87-9 1i8-i5-4,
biological studies 108-:_9-4,
biological studies
103-50-9 108-67-6, bioloqi_al
108-88-3, biological studies
~
~
Go
W
108-94-1, biological studies 108-95-2, biological studies 109-00-
_ 109-06-B 109-08-0 109-73-9, biological studies 109-74-o
109-96-6 109-97-7 109--99-9, biological studies 119-0<.-9
110-00-9D, derivs. 110-02-1 110-02-1D, derivs. 110-59-B
110-62-3 110-83-8, biological studies 110-86-1, biological
4

studies 110-89-4, biological studies 110-93-0 111-26-2
111-27-3, biological studies 111-61-5 111-71-7 111-87-5,
biological studies 112-05-0 112-30-1 112-31-2 112-44-7
112-54-9 114-33-0 116-26-7 117-84-0 119-64-2 120-12-7,
biological studies 120-14-9 120-51-4 120-72-9, biological
studies 120-80-9, biological studies 120-92-3 121-33-5
121-71-1 122-39-4, biological studies 122-78-1 123-07-9
123-08-0 123-11-5, biological studies 123-15-9 123-31-9,
biological studies 123-38-6, biological studies 123-72-8
123-75-1, biological studies 124-07-2, biological studies 124-12-
9 124-13-0 124-19-6 126-98-7 127-91-3 128-37-0, biological
studies 129-00-0, biological studies 131-16-8 132-64-9
134-32-7 135-19-3, biological studies 138-86-3 139-85-5
140-11-4 140-29-4 141-10-6 142-62-1, biological studies
143-08-8 150-19-6 150-76-5 191-07-1 198-55-0 206-44-0
208-96-8 213-46-7 218-01-9 244-63-3 271-89-6 275-51-4
290-37-9 334-48-5 367-47-5 431-03-8 432-25-7 486-25-9
486-56-6 486-84-0 487-19-4 487-68-3 487-89-8 488-17-5
490-79-9 492-27-3 494-52-0 494-97-3 495-40-9 496-11-7
496-72-0 496-78-6 499-74-1 500-22-1 505-57-7 526-75-0
527-60-6 529-19-1 529-20-4 530-57-4 536-74-.3 536-78-7
571-58-4 576-26-1 578-54-1 582-24-1 569--16-2 591-22-0
592-43-8 592-46-1 60)-14-6 603-76-9 613-46-7 614-96-0
620-02-0 620-17-7 620-22-4 620-23-5 621-B2-9, biological
studies 623-36-9 625-30-9 625-33-2
(toxicity of, of tobacco smoke, cfytotoxicity prediction from in
vitro tests in relation to)
IT 625-86-5 628- 73-9 629-08-3 629 -76-5 630-19-3 634-36-6
645-59-0 697- 82-5 698-71-5 771 -51-7 B14-78-8 823-40-5
874-63-5 875- 30-9 875-79-6 928 -68-7 930-68-7 933-67-5
1002-84-2 100 4-66-6 1007-32-5 1196-79-8 1462-64-6 1490-04-6
1570-48-5 1604-28-0 1971-46-6 2016-57-1 2138-48-9
2305-21-7 240 8-37-9 2571-52-0 3189-12-6 4028-66-4 4170-30-3
4360-47-8 4427-56-9 4602-84-0 5724-56-1 5779-94-2
6575-13-9 8000-41-7 8013-90-9 10299-63-5 13730-09-1 15764-1
6-6 15877-57-3 20469-61-8 21296-92-4 21789-36-6 22072-.35-1
22884-95-'3 25309-65-3 27505-78-8 34136-57-7 34136-59-9
B0466-34-B
(toxicity of, of tobacco smoke, cytotoxicity prediction trom in
vitro tests in relation to)
U

ANSWER 3
AN CA102(23):199085j
TI Hypolipidemic effect of propane-1,2-diol on the morphology of rat
erythrocytes
AU
CS
LO
SO Ahluwalia, Pushpa; Amma, M. IG. P.
Biochem. Dep., Panjab Univ.
Chandigarh, India
Res. Bull. Paniab Univ., Sci., 35(3-4),
57-9
SC
DT
CO
I S 4-3 (Toxicology)
J
RBJUAT
0555-7631
PY 1984
LA Eng
AB In rats given 284 mu.L of propane-l,2-diol C57-55-6] in water for
30 days, the levels of total lipids, cholesterol C57-88-57, and
phospholipids of erythrocyte membranes were significantly decreased.
The cells maintained a normal shape but were spurred. Their outer
membrane appeared under the electron microscope as very rough, having
crenations and deformations. Apparently, alterations in the compn.
of the membrane lipids changes the cellular morphol. which is very
essential for the normal metabolic function of erythrocytes.
KW propanediol toxicity erythrocyte; membrane erythrocyte lipid
propanediol
IT Phospholipids
Lipids, biological studies
(of erythrocyte membrane, propanediol effect on, cellular morphol.
in relation to)
IT Cell membrane
(of erythrocyte, lipids of, propanediol effect on, cellular
morphol. in relation to)
IT Erythrocyte
(propanediol toxicity to, membrane lipids in relation to)
IT 57-88-5, biological studies
(of erythrocyte membrane, propanediol effect on, cellular morphol.
in relation to)
IT 57-55-6, biological studies
(toxicity of, to erythrocyte, membrane lipids in relation to)
U-
6

ANSWER 4
AN CA102(3):19302w
TI Developmental toxicity and structure/activity correlates of glycols
and glycol ethers
AU Johnson, E. Marshall; Gabel, Bradley E. C.; Larson, John
CS Daniel Baugh Inst., Jefferson Med. Coll.
LO
SO
SC
DT
CO
Philadelphia, F'A 19107, USA
EHP, Environ. Health Perspect., 57,
135-9
4-6 (Toxicology)
J
EVHPAZ
IS 0091-6765
PY 1984 '
LA Eng
AB Of 14 glycols and glycol ethers tested for embryo and adult toxicity
in Hydra attenata, diethylene glycol C111-46-61, ethylene glycol
monomethyl ether monoacetate C11U-49-6], ethylene glycol monoethyl
ether monoacetate C111-15-9], and ethylene glycol diacetate
C111-55-7] were equally toxic to adults and embryos (the individual
compds. had differing toxicities). Ethylene glycol C1q7-21-1] had
the greatest embryotoxicity relative to adult toxicity. No obvious
structure-activity relations between these compds. and developmental
toxicity were obsd. in this test system.
KW development toxicity glycol ether Hydra
IT 6lycols, biological studies
(developmental toxicity of, in Hydra attenata assay, structure in
relation to)
IT Senescence and Senility
(glycol ethers and glycols toxicity in relation to, in Hydra
attenata assay)
IT Hydra attenuata
(glycol ethers and glycols toxicity to, development in relation to
)
IT Embryo
(glycol ethers and glycols toxicity to, in Hydra attenata assay)
IT Toxicity
(of glycol ethers and glycols, in Hydra attenata assay,
development in relation to)
IT Molecular structure-biological activity relationship
(toxic, of glycol ethers and glycols, in Hydra attenata assay,
development in relation to)
IT 57-55-6, biological studies 107-21-1, biological studies 107-41-5
109-86-4 110-49-6 110-80-5 111-15-9 111-46-6, biological
studies 111-55-7 111-76-2 111-77-3 111-90-0 112-73-2
1 2.^-99-6
(developmental toxicity of, in Hydra attenata assay, structure in
relation to)
7

ANSWER 5
AN
TI
AU
CS
LO
SO
SC
DT
CO
CA102(3):19045q
Ethylene glycol monomethyl ether and propylene glycol monomethyl
ether: metabolism, disposition, and subchronic inhalation toxicity
t
di
s
u
es
Miller, Roland R.; Hermann, Emile A.; Young, John T.;
Landry, Timothy
D.; Calhoun, Linda L.
Toxicol. Res. Lab., Dow Chem. U.S.A.
Midland, MI 48640, USA
EHP, Environ. Health Perspect., 57,
33-9
4-3 (Toxicology)
J
EVHPAZ
IS 0091-6765
PY 1984
LA Eng
AB Short-term and subchronic vapor inhalation studies in rats and
rabbits showed that there are pronounced differences in the toxicol.
properties of ethylene glycol monomethyl ether (EGME) C109-86-4] and
propylene glycol monomethyl ether (PGME) C1320-67-8]. 0verexpnsure
to EGME resulted in adverse effects on testes, bone marrow and
lymphoid tissues in lab. animals. PGME does not affect these
tissues, and instead, overe;;posure to PGME was assocd. with increases
in liver wt. and central nervous system depression. EGME is
primarily oxidized to methoxyacetic acid C625-45-6] in male rats,
whereas PGME apparently undergoes O--demethylation to propylene glycol
C57-55-6]. Since methoxyacetic acid has been shown to have the same
spectrum of toxicity as EGME in male rats, the obsd. differences in
the toxicol. properties of EGME and PGME are thought to be due to the
fact that the 2 materials are biotransformed via different routes to
different types of inetabolites.
K:W ethylene glycol monomethyl ether toxicity; propylene glycol
monomethyl ether metab; ether ethylene propylene glycol toxicity
IT 625-45-6
(as ethylene glycol
relation to)
monomethyl ether metabolite, toxicity in
IT 57-55-6, biological studies
(as propylene glycol monomethyl ether
relation to)
I T 109-86-4 1.;2-0--67-8
(metab. and toxicity of)
metabolite, toxicity in
8

ANSWER 6
G
AN CA101(23):209264n
TI Primary mutagenicity screening of food additives currently used in
Japan
AU Ishidate, M., Jr.; Sofuni, T.; Yoshil:awa, K.; Hayashi, M.; Nohmi, T.;
CS
LO
SO
SC
SX
DT
Sawada, M.; Matsuoka, A.
Biol. Saf. Res. Cent., Natl. Inst. Hyg. Sci.
Tokyo 158, Japan
Food Chem. Toxicol., 22(8), 623-36
17-5 (Food and Feed Chemistry)
4
J
CO FCTOD7 -
IS 0278-6915
PY 1984
LA Eng
AB Salmonella/Microsome tests (Ames tests) and chromosomal aberration
tests in vitro using a Chinese hamster fibroblast cell line were
carried out on 190 synthetic food additives and 52 food additives
derived from natural sources, all of which are currently used in
Japan. Fourteen out of 200 tested in the Ames assay showed pos.
effects and 54 out of 242 were pos. in the chromosome test. Three
additives (erythorbic acid C89-65-67, C102, and beet red) were pos.
only in the Ames test, although their mutagenic potentials were
relatively weak, while 43 additives were pos. only in the chromosome
test. Eleven additives, Ca(OC1)2, cinnamic aldehyde C104-55-2],
L-cysteine.HC1 C52-89-1], Food Green No. 3 (Fast Green FCF)
C2353-45-97, H202, KBrO3, NaC102, NaOC1, NaN02, cacao pigment, and
caramel, were pos. in both the Ames test and the chromosome test.
The usefulness of such primary screening tests combining 2 different
genetic end-points, gene mutation and chromosomal aberration, and
some correlation between mutagenicity and carcinogenicity of food
additives are discussed.
k::W mutagenicity food additive screening
IT Food
(additives, mutagenicity screening of)
IT Oils
(cinnamon bark, mutagenicity screening of)
IT Oils
(clove, mutagenicity screening of)
IT Oils
(coriander, mutagenicity screening of)
IT Oils
(cumin, mutagenicity screening of)
IT Resin acids and Rosin acids GO
(esters, food additives contg., mutagenicity screening o;) QO
IT Apple M
(ext., food additive, m!itagenicity screening of) W
IT Coffee GO
Cola (genus) N
(ext., mutagenicity screening of) QD
GO
IT Anise
9
