Document LppRaVXEBBXzLQkDzdDpaax5X
mak
n Jr. auamtm,
EXPERIMENTAL CONTRIBUTIONS IN IDENTIFYING
BRAIN POTENTIAL CARCINOGENS IN THE
PETROCHEMICAL INDUSTRY
Cesare Maltoni, Adriano Ciliberti. and Donata Carreiti
Institute ofOncology Bologna, Italy
Introduction
Data on the correlation between hair, tumors and ..xcgenous (environmental and occupational) agents are scanty, but extremely sinking.
Historically, Dr. Thomas F. Mancjso '.as the first to id.'ntiiy an eptdemblcgica! relationship between industnal employment in a specific industry Irubber) and the subsequent development of malignant tumors of the brain: In a series of studies, including demographic, retrospective, and cohort longitudinal investigations, a higher risk of death due to tumors of the central nervous system among rubber workers-was established.1-*
Following the experimental results showing that vinyl chloride was producing brain tumors (neuroblastomas).' epidemiological studies demonstrated an increase in brain neoplasias among workers of the vinyl chloride--polyvinyl cnloride industry,4 which was confirmed by many further investigations.
Recently a two-fold increase in brain tumors in several petrochemical plants and refineries in Texas, was found by some U.S. epidemiological groups. This find ing is still under debate (this volume).
So far, only in the case of VC-PVC workers has the direct casual agent been identified. In both the case of the rubber industry and that of Texas petrochemical plants and refineries, workers have been potentially exposed to a multitude of compounds (several known as human carcinogensi: none of them, however, can at present be definitely linked to the excess of brain tumors.
Theoretically, the experimental approach to the study of brain environmental and occupational carcinogenesis may help to do the following:
. to predict the carcinogenic action of environmental agents (identification!; 1 to assess the degree of carcinogenic potential of environmental agents (quantificationl.
in relation to concentration, length of exposure, and so on: 3. to provide the basis for [he evaluation of the relative carcinogenic risk of various
agents: 4. to evaluate the possibility of sincarcinogenetic effects of exposures to different car-
anogenic agents: 5. to help to interpret epidemiological findings showing an increased brain tumor rate
among people exposed to a multitude of compounds: namely, to identify the risky single agent(s): 6. and finally, to provide basic information on the mechanisms of brain carcinogenesis by environmental agents.
The possibility of producing brain tumors in laboratory animals is well known. Many chemical agents, of different types, following direct implantation and general administration, may produce different types of tumors in a variety of experimental rodents (Table 1). Rats, at present, appear to be the most suitable species.
Three industrial compounds, in recent years, have been experimentally shown to produce brain, and brain-correlated, tumors in rats of different hiscotypes: these are bis (chloromethyl) ether, vinyl chloride, and acrylonitrile (Table 2).
216
0077-1923/1103*1-0216 SI '3.0 f 19*1 NYAS
OLI 6953
tONS IN IDENTIFYING 1NOGENS IN THE INDUSTRY
j. and Donata Carretti
>logy ')
N
tors and exogenous (environmental !y striking. he first to identify an epidemiotogim a specific industry (rubber) and . of the brain: In a series of studies, ort longitudinal investigations, a ral nervous system among rubber
that 1 chloride was producing stuu demonstrated an increase nyl chloride--polyvinyl chloride ivestigations. s in several petrochemical plants tpidemiological groups. This find-
has the direct casual agent been and that of Texas petrochemical tally exposed to a multitude of l; none of them, however, can at mors. he study of brain environmental : following:
1 agents (identification): auronmental agents (quantification), ii so on; dative carcinogenic risk of various
feels of exposures to different cat
ling an increased brain tumor rate mds; namely, to identify the nsky
thanisms of brain carcinogenesis by
natatory animals is well known, itrect implantation and general <rs in a variety of experimental tost suitable species, ve been experimentally shown ts or "Vent htstotypes; these
'tut Table 21
H NVAS
Maltoni et of.: Experimental Contributions
217
Table 1 Experimental Chemicals Used to Produce Experimental. Brain Tumors
Experimental Systems
Chemical Substances
Route
Animal Species
Tumors
Aromatic hydrocarbons 20-Methylcholamhrene J-Methylcholanthrene 3,4-Benzopyrene
Direct implantation
Rats Mice Syrian
hamsters
Gliomas Sarcomas
1,2-Benzopyrene
3,4.8,9-Dibenzopyrene
l,2.J.6-Dibenzanlhracene
1 ib-Dibenzanthracene
9.10-Dimethyl-12-benzanthracene
6.9.10-Trimelhyl-l,2-benzanthracene
Derivatives of aromatic hydrocarbons ZV-2-Fluoren y lacetam ide
General
Rats
administration
Gliomas
N.N'-2.7-Fluorcnyibisacelamide
IV-Nitroso compounds Methyl-tf-nitrosourea (MNU)
General
Rats
administration Rabbits
Gliomas Sarcomas
tVjV-Dtmethyi-iV-nitrosourea (DMNU)
/V,JV'JV'-Trintethvl-.V-nitrosourea
(TMNU) Ethyl-nitrosourea (ENU)
Triazenes I -Phenyl-3J-dimethylmazene
General
Rats
administration
Gliomas
Hydrazines 1,2-Diethylhydrazme
General
Rats
administration
Gliomas Sarcomas Neuro-
csthesio-
epitheliomas
I
Ji
!
Tabu 2 | Industrial Chemicals Known to Produce Brain Tumors in Experimental Animals
t Compounds
Route
Animal Species
Turnon
References
it
Bis (chloromethyl) ether Inhalation Rats
Neuroesthesio-
7
epitheliomas
Vinyl chloride
Inhalation Rats
Neuroblastomas (similar to
5,S,9
i human medulloblastomas)
:
Acrylonitrile
Inhalation Rati Ingestion
Gliomas mainly oligodendrogliomas
10.11
1
OLI 6954
Tale 3
The Incidence of Brain Tumors Among Untreated Sprague-Dawley and Wistar Rais at the Institute of Oncology and Tumor Center of Bologna (Italy)
Animals Ral Strain Sex
Ependymomas
Average Latency Time No. No. % 1 Weeks) No.
SpragueDawley M 1,384 J 0.2
1- 1.412 4 0.3
M&F 2.796 7 02
95.0 105.5 101.0
13 8 21
Tumors*
Gliomas
Meningiomas
Average
Average
Latency
1 alency
lime
% (Weeks) No. % (Weeks) No.
09
118 5 10
07
96.6 26
0.6
81.3 9 0.6
117.1 21
0.7
104.3 19
0.7
106.3 47
Total Average Latency lime
% (Weeks)
1.9 107.4 IS 101.3 1.7 104.6
Wistar
M
170 0 --
-
6 3.5
102.5 1 0.6
119.0 7 4.!
104.9
SS69 n o
No neuroblastomas were found.
* m
SS3 3
9 v> r** --
o -- g
2
r- *
v
OPP O
9
4""i r**i at 3 "
Vt g --
o c
ooo
r- --
5 u. ii
2
aw ww*Vi iifilwin i
Maitoni et at.: Experimental Contributions
219
Table 4
The Incidence of Brain Tumors Among Sprague-Dawley Rats, Treated with 1 ml of Olive Oil per kg Booy Wt by Gavage. Once Daily. 4-5 Days Weekly, for
52-57 Weeks
Ependymomas
Tumors*
Gliomas
Meningiomas
Tout
SpragueDaw ley
Rati
Sex No.
Average Latency
No. % (Weeks)
Average Latency
No. % (Weeks!
Average Latency
No. % (Week!)
Average Latency
No % I Weeks)
M 325 F 325 MA F 650
1 0.3 2 0.6 3 0.5
104.0 91.5 95.7
3 0.9 2 0.6 5 0.8
102.0 114.2 106.9
3 0.9 102.3 4 1.2 100.2 7 1.1 101.1
7 2.1 102.4 8 13 101.5 15 13 101.9
* No neuroblastomas were found.
To achieve the above-listed finalities, the experimental investigations, aimed at studying environmental and occupational carcinogenesis, should meet the following prerequisites:
1. i suitable animal model should be used: 1 the spontaneous background lumonsram of the animals employed must be known: 3. the expertmema I protocols and procedures must be kept highly standardized for the
different experiments, performed in the same laboratory. In our opinion, in order to obtain natural, worthwhile, and comparable data, one must:
A. keep the animal alive until spontaneous death: B. perform, at autopsy, careful gross examination: C. trim the organs and make histological sections in a standard way: D. make histological sections, highly representiative of different pans of the brain,
available: and E follow the same histological classification of tumors.
This report presents our data on the incidence of brain tumors in rats, following the treatment with a variety of industrial compounds, given by inhalation and or by ingestion, at different doses and. in some instances, for different durations and with different schedules.
These data have been collected in the framework of a long-term project on industrial carcinogenesis which was started in 1970 at the Institute of Oncology and Tumor Center of Bologna, and is still going on.
OLI 6956
MUrn
iff
Table 5
The Incidence of Brain Tumors Among Sprague-Dawley Rats Exposed by Inhalation to Vinyl Chloride in Air at Various
Concentrations. From 30,000 to I ppm, 4 Hours Daily, 3 Days Weekly, for $2 Weeks*
*
Vinyl Chloride
(ppm)
Animals Sex No.
Tumors
Neuroblastomas
F.pcndymomas
Gliomas
Meningiomas
Average
Average
Average
Average
Latency
Latency
Latency
Latency
Time
Time
Time
Time
No. % (Weeks) No. % (Weeks) No. % (Week*) No. % (Weeks) No.
Total
Average Latency
Time % (Weeks)
tm! 3
o f H cr\ u> U1
30,000 KUXXI 6,(XX) 2,500
500 250
M F Ml
M 1 Ml
M 1 MF
M F MF
M F MF
M 1 Ml
30 1 .10 0 60 1
30 2 10 5 60 7
30 2 30 1 60 3
30 2 30 2 60 4
30 0 30 0 60 0
30 0 10 0 Mi 0
3.3
--
1.7 6.7 16.7 11.7
6.7 3.3 5.0 6.7 6.7 6.7
-- --
-
800 0 .0
800 0
650 0 672 0 66.6 0
750 0 63.0 0 710 0
89.5 0 97.0 2 93.2 2
--0 0 0
-- 0 -0 -0
--
-- ...
-- -- -- -- --
--
6.7 3.3
-- --
-
--
--
-- 0-- --
0--
--
1 3.3 80.0
-- 0-- -- 0-- -- 0--
0-
0-
1 1.7 80.0
-- 0-- -- 0 - -
2 6.7 65 0
--
0--
--
0--
--
5 16.7
67.2
--
0--
--
0--
--
7 11.7
66.0
-- 0--
-- 0 -- --
2 6.7 750
--
1 3.3 115.0 0 --
--
2 6.7 890
-- 1 1.7 115.0 0 --
4 6.7 82.0
--0
-- 0 -- -- 2 6.7 89 5
99.5 0 -- -- 0
--
4 13.3
98.2
99.5 0 --
--
0--
--
6 100
953
--
1 3.3 105.0 0 --
--
I 3 3 1050
-- 0-- --
1 3.3 84.0 1 3.3 840
...
1 1.7 105.0
1. 1.7 - 84.0
2
3.3
94 5
--0
-
0--
--
0--
--
0--
0--
0 --
0 0-- -- 0
M* If
If
V--
3
I0.IMI
M
30
67 650
0
30 3 16.7 672
0--
1 1.7 HO.O
0~ -- o -- -- 2 6.7 65 0
t
6.000 2.500
5U) :vi
MF
M F Ml
M 1 Ml
M 1 Ml
M 1 Ml
60 7 11.7 666
30 2 30 1 60 3
6.7 75.0 3.3 63.0 JO 71.0
30 2 6.7 89.5
30 2 6.7 97,0
60 4
6.7 932
30 0 ,_
30 0
60 0
Mi 0 --.
Ml a
Ml 0
0--
0 0-- 0--
0-- 2 6.7 2 13
0-- 0 0
0 <1 II
--
--
0 -.
0-
- - 0I 3.1 115.0 o -- I 1.7 115.0 0 --
0- - 0-
99.5 0 - - 0 _
99.5 -
-
0-
I 33 105.0 o --
0 I 3.3 1 17 105.0 | / 7
0
-0 n
--
i 16.7
67 2
--
7 11.7
660
-- 2 6.7 750 -- 2 6.7 890
4 6,7 82 0
- 2 67 89 5
--
4 13.3
98 2
--
6 100
953
--1 84.0 1 84.0 2
-- 0 0
33 105.0 3.3 84 0 33 94 5
1 < ii ii
.111 M 1
Ml
HI ii Ml 0 120 0
150 M
60 0
F 60 0
MF 120 0
100 M
60 0
F 60 0
MF 120 0
50 M 180 0 F 180 0
MF 360 0
23 M
60 0
F 60 0
MF 120 0
10 M
Ml 0
1- Ml 0
MF 120 0
5M
Ml 0
1 Ml 0
MF 120 0
1M
60 0
F 60 0
MF 120 0
Conlrolst
M F Ml-
225 0 240 0 465 0
Tuuil
2.025
-- "
___ --
--
-- -- __ -- --
-- --
--
--
--
-- --
--
___ --
--
II -- 0--
-- 0--
0
-- 0-- -- 0--
-- -- __ -- -- -- -- --.
0 0 0
1 0 1
0 0 0
--
-- -- 0.5
0.3 -- -- --
0-M- -- -- 0-- -- 0"
-- 0-- -- 0--
0 ....
-- 0-- 0 --
-- 0-
-- 01 0.4
-- 1 0.2
* Age nf I lie iiiiiiii.iIs .ii siai'l.' 13-17 week \ t Nil Ifc.iliiR'iu
-- --
-- -- -- -- -- 123.0 -- 123,0
-- --
--
-- -- --
--
-- --
--
--
122.0 122.0
II 0 0--
... -- --
0--
--
1 1.7 *120.0
1 as 120.0
1 1.7 0-- 1 0.8
82.0 -- 82.0
2 1.1 2 l.l 4 1.1
108.0 90.5 99.2
0-- 0-- 0--
-- -- --
0-- 0-- 0-
--
---
1 1.7 0-- 1 OK
132.0 --
132.0
1 1.7 0-- 1 08
930 -
93.0
2 0.9 0 2 04
138,0 138.0
0 0-- 0
0-- 1 1.7 1 0.8
I 1.7 0-- 1 0.8
1 0.5 0-- 1 0.3
0-- 0-- 0
0 -1 1.7 l 08
0 -0 0--
0-- 0-- 0--
1 04 3 1.2 4 o,#
-- -- -- 94.0 94.0
102.0 -- 102.0
124.0 --
124.0
-- --
-- 91.0 91.0
-- ~
-- -- --
106.0 113.0 II 1,2
ii
0-- 0~
0 *-- 2 3.3 2 1.7
2 3.3 0-- 2 1.7
4 2,2 2 l.l 6 1.7
0-- 0-- 0--
0-- 1 1.7 1 0.8
1 17 0-- 1 0.8
1 1.7 0-- 1 0.8
3 1.3 4 1.7 7 1.5
-- --
_
107.0 107.0
92.0 -- 920
115.7 90.5 107.3
-- --
....
910 91.0
132.0 --
1320
93.0 -- 930
1273 1155 1204
OLI 6958
nafcgi.'txa
4**' ' AtfV -v4NMMARi*m4
,'A .*V
Tai_e 6
The Incidence of Brain Tumors Among SpragueDawley Rats Exposed v Inhalation to Vinyl Chloride in Air at Various Concentrations, 4 Hours Daily, 5 Days Weekly, for 17 Weeks*
Tumors
0
Vinyl Chloride
Ippnif
Aninrals Sci No.
Neurobljsiomas
Average latency
lime Nu 1 Weeks)
Ependymomas
No. ...
Average Latency
Time
(Weeks)
Gliomas
Average Latency
Time No. (Weeks)
Meningiomas
Average Liiicncy lime No. % (Weeks)
Nu.
Tot*)
Average Latency
Time % (Weeks)
10.000
M 50 F 30 MF 60
3 100 6 200 9 150
6,000 M 50 3 100 F 50 9 30.0 Ml 60 12 200
2.500
M 50 1 50 MF 60
4 133 1 33 5 43
500 M 30 0 F 50 0
MF 60 0
250 M 50 0 -- F 50 0 -- MF 60 0 --
50 M 50 0 -- 50 0 -- MF 60 0 --
ConiroUt M HW 0 _ r H2 0 -- MF 190 0 --
Tout
$50
62 J 750 700
713 7K3 766
45 7 760 6.7.4
-- -- -- -- _ -- -- --
--
--
0_ 00"
0-- 00
0-- 0 -0-
0-- 0-- 0--
0-- 0-- 0--
0-- 0-- 0--
1 09 0-- l 05
--- -- ..
--
-- -- -- --
-- -- -- -- -- -- 1260
--
1260
0 0-- 0-
0-- 0-- 0--
0_ 0-- 0-
0-- 0-- 0--
0 0-- 0--
0-- 0-- 0--
1 09 3 37 4 21
_ -- -
-- ...
-- _
--
-- --
-- -- tooo 817 862
0 1 33 1 1.7
_
60.0 60.0
0 00 -
0-- 0-- 0
--
-- ...
0-- 0-- 0--
0 0-- 0--
0_ 1 3.3 1 1.7
. -- -- _ -- -- _ 130.0 1300
2 1.1 1 1.2 3 1.6
v 46 5 710
61 3
3 100 7 233 10 167
621 73 1 69.9
3 100 9 30.0 12 2U0
713 74 3 76 6
4 1.31 i 1.3 5 63
45 7 760 63.6
0 0-
0--
-
0-- 0--
0--
_
0-- 1 3.3 130.0 1 1,7 130.0
4 37 4 4.9 g 42
99.7 790 894
* Age of ihe animals Hi start. 12 weeks, t No ue.iimciil
OLI 6959
on ou 9 VI *3 8
MO M JO 0
F JO 0 _
_ --
MF 60 0 --
--
0-
0-- 0-- 0--
"
-- --
2M M JO 0 _ F 30 0 --
MF 60 0 --
_ -- --
0-- 0 0--
--
--
M M 30 0 _ F 30 0 --
MF 60 0 --
. _ --
0
0-- 0"
-- --
Controlit M F
106 82
0 0
-- ---
MF 190 0 --
_ _ _
1 0.9 0 1 0.5
126.0
--
1260
Tout
*50
* *
4|f "i V- i
Ihtf
4f|(ftt4U *4
41
4UII
0--
0 0 0--
0 __
0 0--
0 *_ 0 0--
1 0.9 3 3.7 4 2.1
___ --
___
--
_
___ --
100.0 81.7 86.2
0
0-- 0-- 0--
0-- 0-- 0--
0-- 1 3.3 1 1.7
2 1.8 1 1.2 3 1.6
--
-- --
-- -
-- -- 130.0 1300
16.5 710 81.3
I 31 3 13
0 0
_
0--
0 0
_ --
0--
0 1 33 1 1.7
4 3.7 4 4.9 8 4.2
760 03 8
__ _ -- _ _
--
_
1300 130.0
99,7 790 894
fw tm m> i i# n* Tit*
Hni4i.ii
Ha* I inmn 8* Ikhaiais** if* Vinw Ciiititiut in Am ai iOjmuo and ,(*
rrM hm Vahhm lixmaintt SkiiMMJiMtlOO Mmms TmTai-J*
Tumors
Neuroblastomas
Ependymomas
GliomM
Meningioma*
Total
VC Cone <PP"l3 Ekpoiurct
Animal. Sex No.
10,000 4x5x5
6,000 4x5x5
10.000 1 x 4 x 25
6.000 1 x 4 x 25
10.000 4 x 1 x 25
6000 4 x 1 x 25
Control*}
1ot.il
M F MF
M F MF
M F MF
M K MF
M F MF
M F MF
M F Ml
60 60 120
60 60 120
60 60 120
60 60 120
60 60 120
60 60 120
109 120 229
949
Average
Latency No. % Time No. %
(Week.)
0--
0-- 0--
_ --
0-- 0-- 0"
0-- 1 1.7 1060 1 OS 106.0
0-- 0-- 0--
0 0-- 0
-- -* --
0-- 1 1.7 1 0.S
0-- 0-- 0
-- -- --
0-- 0 "" 0--
0-- 1 1.7 1 OS
--
S4.0 S4.0
0-- 0-- 0--
0-- 0" 0--
-- --
--
0-- 1 1.7 1 0.8
0-- 0" 0
-- --
0-- 0-- 0
Average Latency
Time (Weeks)
... --
--
--
--
--
116.0 116.0
-- --
--
-- --
--
83.0 83.0
-- --
No. %
3 5.0 0-- J 2.3
2 3.3 0-- 2 1.7
2 3.3 0-- 2 1.7
1 1.7 0-- 1 0.8
1 17 1 1.7 2 1,7
0-- 0 0--
2 IS i 08 3 13
Average Latency
Time (Weeks)
No.
%
102.3 0 _
-- 0-- 102 3 0 --
755 0 --
-- 0-- 75 5 0 --
92.5 1 1.7 -- 2 3.3 92 5 3 IS
58.0 1 --1 58 0 2
1.7 1.7 1.7
80,0 0
90.0 1
17
85.0 1 OS
-- --
--
114 5 94,0 107.7
0-- 2 3.3 2 1.7
0_ 0-- 06
Average Latency
Time (Weefce)
No.
%
_ 3 5.0
_0 -- 3 2.5
___ 2 3.3 -- 1 1.7 -- 3 2.5
56.0 3 5.0 97.5 3 50 S3.9 6 5.0
7J.0 2 33 1110 1 1.7 93.0 3 2.5
... 1 1.7
580 1 50 5S.0 4 3.3
___ 0 78,0 3 5.0 78.0 3 25
___ 2 1 8 -- i 0.8
3 1.3
Average Latency
Time (Weeks)
102.3
--
102.3
75.5 106.0 85.7
540 1037 78 8
665 II 1.0 81 3
80.0 770 78.0
797 79.7
114 5 94.0 1077
1 Aye (d AiiiiiidU i iijri 13 week*
I t|NAW( (tllK ||l| Jj)|
|*l)
J N> ti(4iHKnl
0969 n o
tlOl ili
Mik
Table 8
*
The Incidence of Bbain Tumors Among Male Wistar Rate Exposed by Inhalation to Vinyl Chloride in Air at Various Concentrations 4 Hours Daily, 5 Days Weekly, for 52 Weeks*
Tumorst
Neuroblastomas
Gliomas
Meningiomas
Total
Average
Average
Average
Average
Vinyl
Latency
Latency
Latency
Latency
Chloride
lime
lime
lime
Time
Group (ppm) Animals No. % (Weeks) No. /ll (Weeks) No. .11 (Weeks) No. % (Weeks)
&
1 I0.D00 .TO T 100 82 0 0 --
1 T.T
650 4
1 .T.T
77.7
2
A,(88)
30 1 T.T k4(> 3 10.0
88.3 0
-
4 13.3
87 2
3
2.5(8)
TO 1 J.I ti*;o 0
--
0--
- 1 T.T 69 0
4
5<N>
TO 0 --
...
0
--
-- 0 --
--0--
...
5 250 TO 0 -
0
0 *"
0
6 50 TO 0 -- -- 0 --
1 T.T
93 0 1 3.3 93.0
7 1 120 0 -- -- 5 4.2 107.6 1 0.8 1100 6 5.0 108 0
8 Controls} 170
0--
--
6
3.5 1025 1 0.6
119.0 7
4.1 104.9
Total
470
* Age of animals al star! 11-I T weeks. 7 No ependymomas were found. } No treatment
OLI 6961
Total
'.AAI 6.000 2.500
500 250 50
1 Controls*
.10 30 30 30 30 30 120 170
470
3 100 1 3.3 1 3,3 0 ___ 0 __ _
0 ___ 0-- 0--
82.0 84.0 690
_
* Age of animal* a( suit 11-13 week*. 3 No ependymomas were found. J No treatment.
10.0 8ft
107.6 102.5
I Wk)
3.3
65.0 4
13.3
77 7
4 13.3
87.2
-- I 3.3 69.0
'1--1 -- 0 -- -- --0
3.3 93.0 1 3 3 93.0 0.8 110.0 6 5.0 108.0 0.6 119.0 7 4.1 104.9
The Incidence or Brain Tumors Amino SrnAOiic-DAWitv Rat* Exkkiu it Inhalation to Vinyliiuna Chlohide in Am at 150, 100 50, 25, and 10 ms, 4 Hours Dailv, 4-5 Days Weekly, fur 52 Weeks*
Ependymomas
Gliomas
Tumors! Meningiomas
* Total
Average
Average
Average
Average
Vinylidene
Animals
Latency
Latency
Latency
Latency
Chloride
Time
Time
Tune
Time
Group
ippnt)
Sex No. No. % (Weeks) No. % (Weeks) No. % (Weeks) No. % (Weeks)
_1
150
M
60 0 __
__
0_
0
__ . 0
--
f
60 0 --
--
0--
-- 0--
-- 0--
--
M* F 120 0 --
0--
-- 0--
-- 0--
2 (0Q M 30 0 __
0 .--
_0
-- 0_
_
F
30 0 --
--
0--
--
1
3.3
108.0
1
3.3 108.0
M4f 60 0 --
~
0--
--
1
1.7
I0H.0
1
1.7 108.0
B 3 50 M 30 0
1
3.3
)) 10
1
33
1270
2
6.7 . 1190
1 30 1 3.3 95.0 1 3.3 840 1 33 1240 3 10.0 101.0
M & F 60 1 1.7 95.0 2 3.3
97.0 2
3.3
125.0
5
8.3 1022
4
25
M 30 0 -- --
0 w.
_0
... 0 __
...
1- 30 0 --
0 -
--0
0
M & F 60 0
-- 0--
-- 0--
-- 0--
--
5
10
M
30 0 __
--
1
3.3
1)10
0
--
-- 1 3.3 II 1.0
F
30 0 ---
--
0--
-- 0--
-- 0--
M & F 60 0 --
--
1
1.7
II 1.0
0
--
1 1.7 II 1.0
6
Controls!
M 1(10 0 --
--
F 100 0 -- --
M A F 2(81 0 --
--
2 2.0 )32 5 I
0-- -- 1
2
10
132 5
2
1.0 52.0 3
1.0
105.0
1
1.0 785 4
3.0 105.7 1.0 1050 2.0 1055
Total
560
* Age of the umiruU a\ *1.111 lf> *cckk
t N*
ViCfc foutul
| No
OLX 6962
HM i*M
Table 10
The Incidence of Brain Tumors Amono Spracue-Dawley Rats Exposed by Inhalation id Ethylene Dichloride in Air at 250, 150, 50, 10, and 5 ppm, 7 Hours Daily, 5 Days Weekly, for 78 Weeks*
Group
Ethylene Dichloridc
(ppm)
Animals Set No.
' Tumorst
Ependymomas
Gliomas
Meningiomas
Total
Average
Average
Average
Average
Latency
Latency
Latency
Latency
Time
Time
Time
Time
Na % (Weeks) No. % (Weeks) No. % (Weeks) No. % (Weeks)
1
250-150
M
90
0 ___
--
F 90 0 -- -
M AF 180
0-- --
S2
50 M 90 0 --
F
90
0--
--
M A F 180
0-- --
3 10 M 90 0 --
F
m
0--
--
M A F 180
0--
-
4
5
M
90
0 ___
--
F 90 0
--
M & F 180
0--
--
5 Controls) M 180 0 --
F 180 3 1.6 100.0
M A F 360
3 0.8 100.0
Total
1,080
0-- 0-- 0--
| 1.1 0 1 0.5
0-- 2 2.2 2 1.1
0-- 0-- 0--
0-- 0-- 0--
___ --
--
155 0 --
155.0
-_
94.0 94.0
-- --
--
0 ___ 0-- 0--
-- --
--
0 ___ 1 1.1 1 0.5
--
97.0 97.0
0 -- ` --a
0--
--
0 --
--
0 0 0 --
-- -- --
1 0.5
86.0
1 0.5 112.0
2 0.5 fe 99.0
0-- 0-- 0--
___ --
--
1 1.1 1550
1 1.1
970
2 1.1 ' 126.0
0-- 2 22 2 1.1
--
94.0 94.0
0-- 0-- 0--
1 0.5 4 2.2 5 1.4
-- --
86 0 103.0 996
--
t No ncurohljsloniiii were found 4 No Irculmcni.
i
,
f
T if * s t
IO Ij 6 9 6 3
r MAF
90 IH0
1 10 M 90 F 90
M 4 F 180
4 5 M 90 F 90
M 4 F 180
5 Controls) M 180 F 180
M & F 360
Total
------ -
1,080
* Agr M Urf ihinuU 41 mm 12 cckt * *** Nwi Uiit wtt ft 1
g 4Wvi
0 0--
0 -a_ 0-- 0--
0 ___ 0-- 0--
0 ___ 3 1.6 3 0.8
--
--
--
___
--
_
1000 1000
0 1 0.5
I*'0
0 2 2.2 2 l.l
94.0 940
0 0
__
0--
r__
0* 0 ___
0--
--
o1U 1 as
-- 97*0 97.0
0-- 0-- 0--
-- --
0-- 0-- 0--
-- --
l as 86.0 1 as 112.0 2 as 99.0
i l.l 155.0 i l.l 97.0 2 l.l 126.0
0 __ 2 2.2 2 l.l
_. 94.0 94.0
0 -_ 0_ 0--
_ ._ --
1 05 86.0 4 2.2 103.0 5 1.4 99.6
Tim II
Tin IwiofNit w gum Tumors Amono Snuuis-Oawuv Rats Exposed r Inhalation to Acrylonitrile in Air at 40, 20, 10, anu 5 ppm, 4 Hours Daily, 5 Days Weekly, por 52 Weeks*
Tumor*t
Gliomas
Meningiomas
Tout
Group
Acrylo-
niinle Cone (ppm)
Animals ____________
Ses No.
Average
Latency Time
No. % (Weeks) No.
Average
Latency Time
% (Weeks) No.
Average
Latency Time % (Weeks)
i 40 M 30 F 30
M4 F 60
2 20 M 30 F 30
M 4 1 60
3 10 M 30 1- 30
M 4 F 60
4 5 M 30 F 30
M 4 F 60
5 CnntritU} M
10
1 Kl
M 4 1 Ml
Tula!
TtX)
2 6.7 75.5 1 3.3 108.0 3 5.0 86.3
1 3.3 96.0 1 3.3 121.0 2 3.3 108.5
0--
0-- 0--
-- -- --
0--
0-- 0
_ --
--
i) --* 0-- 0--
-- -- --
0-- 0 0--
--
-- _
2 6.7
75.5
t 3.3 108.0
3 5.0 86.3
1 3.3
99.0 2 6.7
975
0--
1 3.3 1210
1 1.7 99.0 3 5.0 1053
0_ _ 0
_
1 3.3 115.0 1 3.3 II S.0
1 1.7 1150 1 1.7 115.0
0_
1 3.3 1 1.7
_ 0--
98.0 1 3.3 98.0 1 1.7
98.0 98.0
1 3.3 134.0 1 3.3 1340
0
0--
-
1 1.7 134.0 1 1.7 134.0
* Age of the animals at start; 12 weeks, t No neuroblastomas or ependymomas were found, t No treatment.
O IiI 6964
^
n&mtmrn
ma<*a
Tarie 12
Tut Ihcwwi or Brain Tumou Among Seraoue-Dawley Rah Eiiobb ry Inhalation to Styrene in Air at 300, 200, 100, jo, AND 2} rru, 4 Hours Daily, S Dayi Weekly. w* J2 Weeks*
Glionut
Turnout Meningiomas
Total
Tf
Group
Styrene Cone (ppm)
Average Lslency Time Ses No. No. % (Weeki) No.
Average
Lslency Time % (Weeks!
No.
Average Latency
Time % (Weeks)
1
300
M
30 0
_
--
0 ----
0 ----
F 30 0
-- 0 ---- 0 ----
MtF 60 0
--
0--
0 A-- --
2
200
M
30 0
--
--
0
-- 0 ---
F
30 0
--
--
0 ----
0 *--
Koo
MAF
0--
--
0--
0--
3
100
M F
30 0 30 0
_ _
_
A--
1
3.3 120.0
1
3.3 120.0
3 10.0 112.7
3 too 112.7
M A F 60 0
--
--
4 t.7 114.3 4 t.7 114.5
4
30
M
30 0
--
0 ----
0 ----
F
30 0
--
--
0--
0 ----
M AF to 0 --
0 -- 0--
3 . 25
M
30 0
_
1
3.3 132.0
1
F 30 1 3.3 106.0 0 -- --
1
M A F to I 1.7 106.0
1
1.7 1310
2
3.3 132.0 3.3 106.0 3.3 119.0
6 Conlrolit M F
60 0
to 0
-- --
M A F 120 0
--
-- --
0 --0 ---- 0 ----
0 --0 0 ----
Tolol
420
* Ags >4 iN Animal' il VIAll 11 aVi t Nu MwuihlAAlonui 111 rpcnd|in<HilAi lfe found | Nu Iftiiwini
OLI 6965
4 5 6 Tout
50 25 Control,}
MAF
M F MAF
M F MAF
,A# 60
50 30 60
30 30 60
M F MAF
60 60 120
420
V 0
0 0 0
0 1 1
0 0 0
_ ___
33 1.7
_
Iwo 106.0
3 4
0 0 0
I 0 I
0 0 0
too 112.7 4.7 114.5
i 3 4
3.3 1200 10.0 HIT
4.7 114.5
---- --u. --
--
0_ 0 --_ 0 __
33 13X0 1.7 13X0
1 1 2
3.3 132.0 3.3 106.0 3.3 119.0
---- --
0 -- __ 0 .-- _ 0 __
* Afi of Ihc animal,al uart: I) wccki t No iwuroblattoma, or ependymoma, were round I No treatment
t
r
c
Table 13 The Incidence of Brain Tumor* Amono Sprague-Dawley Rats Exposed by Inhalation TO Propylene in Air at 5,000, 1,000, and 200 ppm, 7 Hours Daily, 5 Days Weekly, for 104 Weeks*
Tumorst
-- *---
Gliomas
Meningiomas
Total
Group
Propylene Cone (ppm)
Animat, Set No.
Average Latency
Time No. % (Weeks)
Average Latency
Time No. % (Weeks)
Average Latency
Time No. % (Weeks)
1
5,000
M 120
F 120
MAF 240
2 1.000 M too 1' MR)
MAF 200
3 200 M 100 F MX)
MAF 2<R>
4 Control,} M 120 F 120
MAF 240
0-- 0--
0--
0 00"
0 0-- 0--
2 1.7 1 0.8 3 1.2
--
--
-
--
-- --
--- --
108.5 88.0 101.7
0-- 0-- 0-
0 1 10 1 0.5
0--
0-- 0--
0-- 0--
0--
--
-- -
_
II 1.0 II 1.0
-- ""
-- --
-
0_ 0--
--
0-
0_
1 1.0 1110
1 0.5 II 1.0
0
0 ...
0-
--
2 1.7 108.5
1 0.8
88.0
3 12 101.7
Total
HH0
o * Age of (he animals al start 17 weeks,
H t No neuroblastoma* or ependymomas were found. | No treatment.
o\ io <T\ o\
I
;
l
,iiNrtiwftiiTfrti^rw-n^
i `*n*"*
MM
Table 14
.
#
The Incidence of Brain Tumors Among SpraOUE-Dawley Rate Exposed ry Inhalation to Trichlorofluoromethane in Air at 5,000 and 1,000 ppm, 4 Hours Daily, 5 Days Weekly, for 104 Weeks*
Tumorst
Group
Tnchlofofluro*
methane Cone (ppm)
Animals -----------------------
Sea No.
Ependymomas
Gliomas
Meningiomas
Total
Average
Average
Average
Average
Latency
Latency
Latency
Latency
Time
Time
Time
Time
No. % (Weeks) No. % | Weeks) No. % (Weeks) No. % (Weeks)
81
5.IKI0
M
r
90 0 _ 90 0 --
0-- 0--
--
0 2 2.2
90.0
0 -2 2.2
900
M&1
1X0
0--
--
0--
-
2 l.l 90.0
2 l.l
90.0
2
1.01X1
M
90 0 --
2 2.2 129.5
1 l.l 720
3 3.3 110.3
F
90
1 LI 103.0 1 1.1 75.0 1 LI XX 0
3 3.3 XX 7
M&F
1X0
1 0.5 103.0 3 1.7 II 1.3 2 l.l X00
6 3.3 99.5
3 Controls! M F
M&F
150 150 300
1 0.7 94.0 1 0.7 840 0 --
0--
~
2 1.3 82.5 0 --
1 0.3 940 3 1.0 83.0 0 --
-- --
2 1.3 2 13 4 1.3
89.0 82.5 85.7
Total
660
* Age of the animals at start V 1 .1 weeks,
t No neuroblastomas were (ouiul t No treatment The same control group is common for the experiments ECU and FCII.
O LI 696
2 3 Total
r M&F
1,000
M F M Sl F
Controls}
M F M&F
90 1X0
90 90 180
150 150 300
660
0-- 0--
0-- 1u 1 0,5
1 0.7 0-- 1 0.3
-- --
103.0 103.0
94.0
--
940
-0-- 0-
2 2.2 1 l.l 3 1.7
1 0.7 2 1.3 3 10
-- --
129.5 75.0 1)1.3
840 *2.5 83.0
0-- 2 2.2 2 1.1
1 l.l 1 l.l 2 l.l
0_
0. 0_
Age uf ihc animats at start 9 11
N.i neuti>Mjsi..niat weie found
N>
|h MIM
gioup II common for the cipeitmcnls FC12 ami Fell
-- 90.0 90.0
720 88.0 80.0
-- -- --
0_ 2 22 2 II
3 3.3 3 3.3 6 3.3
2 1.3 2 13 4 1.3
90.0 90.0
110.3 88.7 99.5
890 82.5 857
Table IS*
The Incidence of Brain Tumors Amono Spradue-Dawley Rats Exposed by Inhalation to Dichuiroohluorcrhethane in Air at 5,000 and 1,000 ppm, 4 Hours Daily, 3 Days Weekly, for 104 Weeks*
Group
Dichlorortuoro-
methane (ppm)
Animals Sex No.
1 2 3 Total
5,000 I.IXXI Controls}
M 1 M&F
M IM&F
M F M&F
90 90 180
90 90 180
150 150 300
660
Ependymomas
Average Latency
Time No. % (Weeks)
0 ___ 0-- 0-
0 0-- 0--
1 0.7 0-- 1 0.3
_
--
-- --
-- 940
--
94.0
Tumorsf
Gliomas
Average Latency
Time No. % (Weeks)
1 1.7 1090 l 1.7 970 2 1.7 1 13(1
3 33 1(81.4
1 l.l
90.0
4 22
97.8
1 0.7 2 13 3 1.0
840 82 5 83.0
* Age of the animals ul slarf;9 -13 weeks, t No neuroblastomas or meningiomas were found. ; No treatment. The same control group is common for the experiments FCI2 and FC'I. .
Total
No. %
Average Latency
Time (Weeks)
1 1.7 I 1.7 2 1.7
3 33 1 l.l 4 2.2
2 1.3 2 1.3 4 1.3
1090 97(1 1030
1(81.4 900 97.8
89.0 82.5 857
6969 110
sms,
MM
Table 16
4
The Incidence oe Bbain TiuoAS Among Sprague Dawley Rats Exposed bv Inhalation to Chlokopiploobomethane in Aw at S.000 and 1,000 ppm. 4 Hooks Daily, 5 Days Weekly, km 104 Weeks*
Tumoist
Epeniiymomo
Gliomas
Meningioma*
Total
Group
Chloro difluoromethane
(ppm*
Animals Sen No
Avenge 1 atency
Time No. % (Weeks)
Average Latency
Time No % (Weeks)
Average Latency
Time No % (Weeks)
Avenge Latency
Time No. `J-li (Weeks)
1
i.uo
M 60 0 ,,
2 13 78.5
0--
2 33
78.5
fci
60 1 1.7 460 0
2 1.3
W5
3 5.0 101 7
M A 1 1:0
1 OK 460
2 1.7 78.5
2 1.7
VV>
S 4.2
42 4
2
1.000
M 60 0
0*
1 1.7 124.0
1 1.7 1240
1 60 0 -
0 ...
--
0 --*
0 --
M & 1 120
0-
-
0-
1 01 1240
1 OK 1240
J Controls) M 60 0 --
1
60
0_
--
M A F 120
0-
-
0-- 0-- 0--
--
--
01 17 t 0.8
136.0 1360
0 1 17 1360 1 OK 1360
Total
360
* Age of an.mals at start H week*, t No ncuioHakloinus were found \ No treatment.
----------------- V f r if ilr t i l l I Ir
l.
n
2 3 Total
1,000 ConlruliJ
M F MA F
60 to 120
M F M(F
to to 120
260
* Age of animal* at sun: 8 weeks,
t No neuroblastomas were found. J No Ireatment.
000--
0-- 0-- 0~
_ _ _
-- _ --
1, / /* >
---- "
---- -- "
2 1.7
1 1.7 0 ~~ 1 0.8
01 1.7 1 08
99.J
1240 -- 124.0
--
1360 IJ6.0
j 42
*2.4
i 1.7 124.0
0 ___
1 0.8 124.0
0 __ 1 17 1 0.8
1360 1360
Ini iium i m Kaain Iimmi Awimi
Hfv I iham i ls<uhuh n \tMi t hi. <** Ou
at 50.01. 14.65, .1)1, 10, 0 3, anp 0.03 mc/ku Buoy Wr. Omc Daily. 4 3 Days Wijilly. h 52 M Wilts*
Turnout
Croup
Vinyl Chloride Ingested img/kg body wi)
Ependymomas
Glioma*
Meningiomas
Animals
No. at Sex Start No.
Average Latency
Time (Weeks)
No.
,,
Average Latency
Time (Weeks)
No.
Average Latency
Time (Weeks)
No
Total
Average Latency
Tune % (Weeks)
1 2 J 4 5 6 7 Total
50.00
M F MF
1665 M F MF
3 33 M F Ml
10 M F Mb
03 M 1 MF
0.0) M F MF
Controls^ M F
MF
40 40 80
40 40 80
40 40 80
75 75 150
75 75 150
75 75 150
115 115 230
920
00-- 0'
0-- 0-- 0-
1 2.5 0-- 1 II
, 1.3 0-- 1 07
0_ 0-- 0-
0 2 27 2 13
i 09 | 09 2 09
-- -
--
92,0
92.0 1150
--
1150
--
--
90 5 90.5 1040 87.0 95.5
0_ 0-- 0 --
0-- 0-- 0-
0-- 0-- 0-
1 13 0-- 1 07
4 5.3 2 2.7 6 4.0
0-- 0-- 0-
i 09 2 1.7 3 13
_
-
--
-
~ 121.0
--
121.0 96.7 96.5 96.7
--
-108.0 1142 112.0
0 I 25 1 1.2
1 25 0-- 1 12
0-- 0-- 0"
0-- I 1.3 1 07
0-- 0-- 0-
0-- 0-- 0--
1 09 1 0,9 2 09
0 590 1 59,0 1
1200 --
1200
1 0 1
-- 11 -0
1
-2 710 1 710 3
_4 --2
t
--o
--2 2
76.0 3 92.0 4 840
-- 25 1.2
25 -- 1.2
25
12
2.7 1.3 20
53 2.7 4.0
--
27 1.3
2.7 3.4 30
-
59.0 590
120.0 --
120.0
93,0
92 0
imo 710 102 3
967 965 967
--
*05 90.5
960 101.8 993
Ag. i4 tniouli ii ti<i(i 10 llcckt
t Ni uciniiNaUiMit.it vtcic I*>un4 J (Kite ml
OLI 6970
yfufiaYwttiui
i*"* `T
i *' ' ' * *v.is Mi*
Tabu 18
The Incidence of Bbain Tumou Among Spraque-Dawuv Rato, Exposed by Ingestion to Vinylipcne Chlobide in Ouve Oil at 20, 10,5. 0.5 mg/kg Bogy Wt, Once Daily, 4-5 Days Weekly, lot 52-59 Weeks*
Tumorsf
"
#
Vmyhdcnc Chloride Ingested
ImgAg body wl|
Animals
No. *i Su sun
Ependymomas
Gliomas
Meningiomas
Total
Average
Avenge
Average
Average
Latency
Latency
Latency
Latency
Time
Time
Time
Time
No. % (Weeks) No. % (Weeks) No. % (Weeks) No. % (Weekl)
1 20
M
F
M&F
2 10
M
F
M)
2s M 1
MAF
4 OS M F
M 2k F
5 Controls} M F
MJF
Total
50
so
100
so so
100
so so
100
so so 100
>75 175 350
750
0_
0-
0--
0 0--
0--
1 2.0 0
1 1.0
0
0-- 0-- 0-- 1 06 1 0.3
"
160
--
#6.0 --
-- 87.0 87.0
0_ 0 ...
0--
--
0 0--
0--
0_ 0--
0-
--
--
_
-
1 2.0
0 1 10
80.0
-
800
2 II 109.5 2 l.l 114 2 4 1 1 111.8
0_ 0-- 0--
--
0--
0--
0--
--
1 2.0 1110
0 --
1 10 1110
1 2.0 II 1.0
0 " I 1.0 II 1.0
1 2.0 1 20 2 20
121.0 IIH0 INS
2 40 103 5
1 20 into 3 30 ions
0
0 0-
1 20
0 1 10
no #0
2 l.l 1130 4 2.3 1112 4 23 iao.s 7 40 102 5 6 17 1047 ii 31 lOS.g
* Age of .iniffltib .il tiarl: 9 10 vii'ek^ No ncuiohUMontJi were found J OllVC Oil
O L I 6973.
' * S Tail
*M F
M* F
0.5 M F
MAF
Control*} M
F
Mtr
30 50 100
50 50 100
175 175 350
750
* A(C ofanimal* *1 sun: 9-10 week* No ncurohlmoaMi were found } Olive oil
1 20 0 1 1.0
0 0 0--
0 1 0.6 1 0.3
1_60
860
--
87.0 87.0
---- --
--
2.0 #00 -- 1.0 <0.0
II 109.5 l.l 114.2 II 111.8
1 2.0 1210
1 2.0 111.0
2 2.0 119.5
0_ -
0-- 0--
2 1 1 113.0 4 23 100.5 6 1.7 104.7
< l-U 1(1.0
2 4.0 103.5 1 2.0 1)8.0 3 3.0 I0< 3
1 2.0
01 to
g.O
--
<0
4 23 7 4.0 II 3.1
1112 102.5 I0S.S
Tail* 19
Tut Incidence or Brain Tumor* Amono Sfraoue-Dawlev Rata ExKmep y Inciextion to Acryumiwuli in Olive Oil at 5 mo/ko Bout Wt, 3 Time* Weekly tor 52 Week*
Group*
Acfylonilrile Dote
(mg/kg body wt)
Animal* -------- -----------
No. at Sea Start
l 5 M 40 F 40
M AF <0
2
Control*)
M
75
F 75
M AF 150
Total
230
rbiem = = .= ---------- =.-~
----
Age ol the animal* at Hart: 10 week*, t No ncoroMatlomat were found. } Olive oil.
Ependymoma*
Glioma*
Turnout Meningioma*
Toial
Average
Average
Average
Average
Latency
Latency
Latency
Latency
Time
Time
Time
Time
No. % tWeck*) No. % (Week*) No. % (Week*) No. X (Week*)
0 ___ 0-- 0--
_0 0___ ___ ___
___
-- 1 2.5 430 0 -
1 1.3
430 0
0--
-
-- 1 H 430
-- I 1.3 43.0
0--
-- 1 1.3 logo 1 1.3 76.0 2 27 920
1 1.3 <7.0 2 2.7 1142 1 1.3 920 4 5.3 1017
1 0.7 <7.0 3 . 2.0 112.0 2 1.3 <4.0 6 40 )
o> VO -o (O
i
1
'i
r-
2
i
.
N*>
T*u 20
The Incidence of Brain Tumors Among Sprague-Dawley Rate, Exposed ry Ingestion to Styrene in Olive Oil at 2SO and SO mg/kg Body Wt. Once Daily, 4-S Days Weekly for 52 Weeks*
Tumorsf
Group
Styrene Dose
Ingested Ung/lg body wt)
Ependymomas
Gliomas
Meningiomas
Total
Animals
Average Latency
Average Latency
Average Latency
Average Latency
No. at
Time
Time
Time
Time
Sex Sturt No. % (Weeks) No. % (Weeks) No. % (Weeks) No. % (Weeks)
1 250 M 40 0
0
1 2.5 90/:
1 2.5
900
ts Qs
F
40 0 -- -
0--
--
1 2.5 10.10 1 2.5 1010
M * F HO 0 --
0--
2 2.5 9li5
2 25
965
2 SO M 40 0 --
1 2.5 106.0 0 --
-
1 2.5 1060
F
40 1 2.S 82.0 0 -- --
3 7.5 l32/ 4 10.0 1195
M 2k F HO 1 1.2 82.0 1 1.2 106.0 3 3.7 1321 5 6.2 116 8
3 Controls^ M
40 0 -- --
0--
--
0--
-
F 40 1 2.5 96.0 0
-- 0--
M & F 80 1 1.2 96.0 0
-' 0 --
--
0-- 1 25 1 1.2
960 96.0
Total
240
* Age of Ihe animals al start: 13 weeks, f No neuroblaslomas were round ; Olive oil.
OII 6973
91^ Q vi oe O O ^o ;og* 2i 2i * I1 os <ost.
<WNi <--N
;s (Ss iii <' <PN fI <-: r*ri [IIiIi
* f*t O n n OOO
1 1 iM I S I2 M i -- O -- OOO
PP J oo SS i *
?g 3 * Sto St 552
(2
Controls}
-3 o fi _3 3u *W (3 o6 E c jg -s *1-
i I!
g,o <20
-A-: MM
Maltoni ec a/.: Experimental Contributions
237
Table 21
The Incidence of Brain Tumors Among Sprague-Dawley Rats, Exposed by Ingestion to Styrene Oxide in Olive Oil at 250 and 50 mg kg Body Wt, Once Daily, 4-5
Days Weekly, for 52 Weeks*
* Group
Styrene Oxide Dose (mg/kg body wti
Animals
No. at Sex Start
Meningiomast
Average Latency
Time No. % (Weeks)
i 250 M 4ri 0
--- *
F 40 2 5.0 129.5
MAF SC 2 23 129.5
2 50 M 40 1 15 107.0 F 40 l 15 126.0
! MAF SO 2 15 116.0
3
Controls}
M
F
MAF
40 1 . IS 40 0 --
SO I 1.3
S1.0 --
81.0
Total
240
* Age of the animals at start: 13 weeks,
t No neuroblastomas, ependymomas, or gliomas were found. } Olive oil.
Plan of the Studies: Materials and Methods
The incidence of brain tumors has been systematically studied in our Labora tory for the following:
1. untreated rats I Sprague-Dawley and Wislari; 2. rats (Sprague-Dawleyl treated with virgin olive oil which is the vehicle used for (he
ingestion fgavage) experiments: 3. rats (Sprague-Dawley and. in ihe case of vinyl chloride, also WislarL treated by
inhalation at ditfetent doses (and, in the case of vinyl chloride, also for different limes and with different schedulesl with:
i A. vinyl chloride. B. vinylidene chloride: C. ethylene dichlonde, D. acrylonitrile. E. styrene. F. propylene, G. trichlorofluoromethane(FC UL H. dichlorodifluoromethanelFC 12L I. chtorodiRuoromeihanelFC 22):
4. rats (Sprague-DawleyI. treated by ingestion at different doses with:
A. vinyl chloride. 8. vinylidene chloride. C. acrylonitrile.
1 t 1
OLI 6974
J.
iT
\
238 Annals New York Academy of Sciences
0. styrene, E. styrene-oxide. F. vinjlidene fluonde, G. trichloroethylene, H benzene, 1. 'asbestos (Crocydolitet, J. polyvinyl chloride (PVC).
All the supplies of the compounds used were examined in order to determine whether they meet the required standards.
The concentrations, when the compound was administered by inhalation, were controlled by continuous gas chromatographic monitoring..
Treatment was always performed by the same people. This is particularly im portant for gavage, since the animals become accustomed to the same operator.
The animal breeds have been routinely employed in our Laboratory for many years. It should be pointed out that, whatever their use. all the animals of our colony undergo periodic examination and complete autopsy, giving us extensive infor mation concerning their pathology.
The age of the animals in the experiments considered in this report, at the start of treatment, varied from II to 16 weeks.
The animals were kept alive until spontaneous death. Every two weeks, they were submitted to an examination for the detection of any gross changes.
Full autopsy was performed on each animal. Ai! the different parts of the body were explored, and specimens for histology were taken from all major organs and any other organ with pathological lesions. As far as the brain was concerned, careful gross examination was made, and all lesions, either superficial or discovered bv dissecting the organ (after fixation) were measured and described.
The brain was always trimmed in a standard way. and sections were routinely stained with hematoxylin-eosin and, when necessary, with special techniques.
The criteria for histopathological characterization and classification of brain tumors were kept standard for all the experiments.
The observed tumors were grouped in four major categories: neuroblastomas (similar to the human medulloblastomas), ependymomas, gliomas, and meningi omas.
Gliomas and meningiomas in the original records were also subclassified ac cording to histotype. The distribution of the different histotypies in those two cate gories of tumors, however, did not seem to be relevant. Most of the gliomas are oligode nd rogliomas.
Results*
The incidence and the latency time of brain tumors among 2,796 SpragueDawley and 170 Wistar untreated rats in our colony, and among 630 SpragueDawley rats following long-term treatment with olive oil, by gavage, are given in Tables 3 & 4. respectively.
The incidence of these tumors appears to be higher in Wistar rats (whose number, however, is lower). The treatment with olive oil does not appear to affect the onset of brain tumors.
Tables 5-t6 give the results of the experiments studying the effects of the exposure by inhalation to the following: vinyl chloride (Tables 5-8), vtnvlidene
* The incidence of the tumors is referred to the total number of animats at stan: the time of latency as age of the tumor-beanng animals.
OLI 6975
* t0UI number of animal! at start; the time
-- 3. 8.3 o-- 28 3. 5 8-k ^c H S'
5:
,yi aa0O A
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J2".#3') o!
S'as p3
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sr|t
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#9 ^ 31 aa.;s ?o'*
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og'i5s |a5- ^K Ef => 2," (3U 3-B Cnl ,,c Zo-2 3n-S3 gr->
*s 5_
oo,,naO. 38
a!5*c2n oaP-SS.i**?0 gS8-.32? QI?.Z ? gli^teas^l
3- </
^s3a
as3 oc^-Ir BA ET 2.o 32 *6
fpS-B fi-s
3a"
.' 3e
oir a` 25 A
52 S|!E -g s g{a/> =gmasoJsS '3SS0<
O0< 3Adnq-0\ *"0* 1
A 4 P 3" w 382
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r 4 I
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s
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ao
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y o
if
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O t* H o\ \o -O C\
Table 22
The Incidence or Brain Tumors Among Smlagub-Dawley Rats, Exposed by Ingestion to Vinyudenb Fluoride in Olive Oil
at 8.25 and 4.12 mg/kg Body Wt, Once Daily, 4-5 Days Weekly, for 52 Weeks
*
Group
Vmylidcne Fluoride
Dose
(mg/kg body wt)
Animal!
No. at Sex Start
1 2 3 Total
8.23 4.12 Control!
M F M&F
M F MiF
M F MAF
35 35 70
30 30 60
30 30 60
190
Ependymomas
Average Latency
Time No. % (Weeks)
1 2.8 1130
0--
--
1 1.4 1130
0 ___ 0-- 0--
-- --
--
0-- 0-- 0--
--
-- --
Turnout
Gliomas
Meningiomas
Average Latency
Time No. /. (Weeks)
Average Latency
Time No % (Weeks)
0-- 0-- 0--
0 1 3.3 1 1.7
1 3.3 0-- 1 1.7
_ -- --
-- 116.0 116.0
87.0 -- 87.0
0-- 0-- 0--
0-- 0-- 0--
0-- 0-- 0--
-- -- ~
-- -- --
-- -- --
Total
Average Latency
Time No. % (Weeks)
1 2.8 0-- 1 1.4
0 1 3.3 1 1.7
1 3.3 0-- * 1.7
113.0 "
1130
-- 116.0 116.0
87.0
87.0
* Age or the animats al start: 13 weeks, t No neuroblastomas were found.
;
\ <
;
*
>
-lM J'j t W W r jW Pi
1 * 'm i ij m m w m
Table 23
The Incidence of Bbain Tumors Among Sprague-Dawixy Rais Exposed by Ingestion to Tkichlokoethylene in Olive Oil at 250 and 50 mo/ko Body Wt, Once Daily, 4-6
Days Weekly, tor 52 Weeks*
Group ,
2 3 Total
Trichloro ethylene
Dose (mg/kg body wt)
250
50
Controls^
Animals
No. at Scs Start
M F MAF
M F MAF
M F MAF
30 30 60
30 30 60
30 30 60
180
Gliomas
Average Latency
Time No. % (Weeks)
0 ---- 0 ---- 0--
1 3.3 100.0 0 ---- 1 1.7 1000
1 3.3 87.0 0 ---- l 1.7 87.0
Tumorst
Meningiomas
Average Latency Time No, % (Weeks)
0-- 0 ---- 0 ----
0 ---- 1 3.3 108.0 1 1.7 108.0
0 ---- 0 ---- 0 ----
Total
Average Latency
Time No. % (Wccksl
0 ---- 0 ---- 0
1 3.3 100.0 1 3.3 1080 2 3.3 104.0
1 3.3 0 . --1 1.7
87.0 --
87.0
* Age of the animals at slurI: 13 weeks, t No neuroblastomas and ependymomas were found.
{ Olive oil.
'j^ i "
i
h
OLI 6977
* i Total
<H Citniiiiui
M* I
M I M A I'
M ! MAP
Ml
HI III Ml
.Ml 30 AO
180
II
1 11 IIMIII II 1 1.7 urn ii
1 3,3 87.0 0 ---- 1 1.7 87.0
* Age of the animals n start: 13 weeks,
t No neuroblastomas and ependymomas were found t Olive oil.
i
< i Iihiii I U Him ii
0 0---- 0----
(i H
1 11 imiti 1 4 1 III* II i It IlMH
1 3.3 *7.0 0 1 1.7 87.0
Table 24 The Incidence of Brain Tumors Among Sfrague-Dawley Rats Exposed by Ingestion to Benzene in Olive Oil
AT 250 AND 30 MG/KG BODY WT ONCE DAILY, 4-5 PAYS WEEKLY, FOR i2 WEEKS*___________ ^
Tumorst*
Group
Benzene Dose
(mg/kg body wt)
Animals
No. at Sex Slarl
Gliomas
Average Latency
Time No. % (Weeks)
Meningiomas
Average Latency
Time No. % (Weeks)
Total
No.' %
Average Latency
Time (Weeks)
1 2 3 Total
230 M F
MAP
30 M F
MAP
Controls}
M |*
MAP
35 35 70
30 30 60
30 30 60
190
i 2.8 0-- 1 1.4
0-- 0-- 0--
1 3.3 0-- 1 1.7
157.0 157.0
--
87.0
--
87.0
0--
--
1 2.8 123.0
1 1.4 123.0
1 3.3 0-- 1 1.7
1 50 115.0
0 -0-- 0--
--
-
1 2.8 1 2.8 2 2.8
157.0 123.0 1400
1 3.3 115.0 0-- 1 1.7 1150
1 3.3 0" 1 1.7
87.0 87,0
* Age of the animals at star1: 13 weeks, t No neuroblastomas or ependymomas were found. { Olive oil.
OLI 6978
-<' .V>.- */**,,
Table 25
#
The Incidence of Brain Tumors Among SpraGue-Dawley Rats Exposed by Ingestion to 2 mg of Asbestos (Crocydoute) in Olive Oil, Once Every Two Weeks, for 52 Weeks*
Ependymomas
Group
Animals
Average Latency
No. al
Time
Sex Start No. % (Weeks)
HI 2 mg
M
Ashcsios F
(Crocy- M & F
iloltlu)
(2) Controls M
(olrvc
F
oil) M&F
40 40 BO
75 75 150
0_ 0--
0
0--
1 1.3 1 0.7
_
--
--
S7.0 87.0
Total
230
Turnout
Gliomas
Meningiomas
Average Latency
Time No. % (Weeks)
0_ 0 -- 0--
-- --
Average Latency
Time No. */. (Weeks)
0_ 0--
0
--
1 1.3 108,0 2 2.7 114.2 3 2.0 112.0
1 1.3 760 1 1.3 92.0 2 1.3 84.0
Total
Average Latency
Time No. (Weeks)
0_ 0--
0--
_ --
--`
2 2.7 92.0 4 5.3 101.7 6 4.0 98.5
* Age of ihc animals ai sun: 10 weeks, t No neuroblastomas were found.
O LI 6979
II) 2 mg
M
Arbeslos F
(Crocy. MAF
dolitc)
40 40 80
(2) Controls M
(olive
F
oil) M A F
75 75 ISO
Total
230
0 0-- 0--
0 ___ 1 13 1 0.7
__ ___ --
___
87.0 870
* Age of the animili at siart: 10 weeks, t No neuroblastomas were found.
0--
--
0 --. --
0
1 1.3 108.0 2 2.7 114.2 3 2.0 112.0
0-- 0-- 0--
--
--
--
1 13 76.0 1 13 92.0 2 1,3 84.0
0 ___ 0-- 0--
-- --
2 2.7 92.0 4 5.3 101.7 6 4.0 98.5
Table 26
The Incidence or Brain Tumors Among Sprague-Dawley Rats, Exposed by Ingestion to Polyvinyl Chloride
(2 mg in Olive Oil), Once Every Two Weeks for 52 Weeks
*
Group
PVC Dose
Animals
No. at Sex Start
Ependymomas
Average Latency
Time No. % (Weeks)
Tumorat
Gliomas
Meningiomas
Average Latency
Time No. % (Weeks)
Average Latency
Time No % (Weeks)
Total
Average Latency
Time No. % (Weeks)
1 2 3 Total
2 mg (suspension)
2 mg (emulsion)
Controls}
M F M 2k F
M F M&F
M F MAF
20 20 40
20 20 40
75 75 150
230
0 0-- 0--
0-- 0 0--
0 l 1.3 1 0.7
--
--
--
-- -- -- 87.0 87.0
0-- 0-- 0--
0-- 0-- 0
--
-- -- -- --
1 1.3 1080 2 2.7 114.2 3 2.0 112.0
0-- 0 0
0 0 -0--
1 1.3 1 1.3 2 1.3
...
-- --
-- -- *--
76.0 92.0 84.0
0-- 0 0--
0-- 0-- 0--
2 2.7 4 5.3 6 4.0
--
--
--
-- 920 101.7 98.5
0 * Age of the animals at slarl: 10 weeks, t No neuroblastomas were found.
H { Olive oil-
01 to
00
o
i
c,
rigVfc A
........... - -
^ niriJiuLnfim a <i
244 Annals New York Academy of Sciences
Tasle 27 The Incidence of Neuroblastoma is Spragle-Dawley Rats is ReLaiios to
CONCENTRATION OF VlNYL CHLORIDE ADMINtSTERED BT ISKALATIOS.FOR 52 WEEKS
Experiments
Vinyl Chloride (ppm)
BT 6 BT1
BT 2
BT 1, BT 9 BT IS
Controls BT 1, BT 2, BT 9, BT IS
30.000 10,000 6,000 2JOO
500 250
200 ISO 100
50
23 10 3
l
0
% Animals with
Neuroblastoma
M FT
3J --- 1.7
6.7 16.7 11.7 6.9 3.3 XI 6.7 6.7 6.7 -- ---- ----
-- ----
-- ---- -- ----
----
-- ---- -- ---- -- ---- -- ----
chloride (Table 91, ethylene dichloride (Table 10), acrylonitrile (Table 11). styrene (Table 12), propylene (Table 13V, tnchlorofluoro methane (Table 14), diehiorodifluoromethane (Table 15), and chlorodifluoromethane) Table 16).
Under our experimental conditions, only two of the above-listed compounds, given by inhalation, appear to produce brain tumors, namely vinyl chloride and
acrylonitrile. Vinyl chloride appears to produce neuroblastomas both in Sprague-Dawley
and Wistar rats, at a concentration of 30,000. 10.000, 6,000, and 2,500 ppm, when given for 52 weeks, 17 weeks, or less.
Acrylonitrile produces an increase in the incidence of gliomas (oli
godendrogliomas) at 40 and 20 ppm. Tables 17-26 present the results of the experiments studying the effects of the
exposure by ingestion to the following: vinyl chloride (Table 17), vinylidene chloride (Table 18), acrylonitrile (Table 19). styrene (Table 20), styrene oxide (Table 21). vinylidene fluoride (Table 22), trichloroethylene iTable 23), benzene (Table 24). asbestos (Crocydolite)(Table 25). and polyvinyl chloride (Table 26),
Under our experimental conditions none of the above-mentioned compounds, given by ingestion, seemed to produce brain tumors.
idcmy of Sciences
27 raGUE-Dawley Rats in Relation to mstered *y Inhalation, for 52 Weeks
% Animals with
Neuroblastoma
M FT
3.3 -- 1.7 6.7 167 11.7 69 3J 5.1 67 67 67
-- ---- -- ----
_-- --
-- ---- -- ----
----
_-- --
-- ---- -- ---- -- ----
----
I
i
|
T %
j !
1 i
-E 10), acrylonitrile (Table 11), styrene luoromethane (Table 14), dichlorodimethane (Table 16). y two of the above-listed compounds, m tumors, namely vinyl chloride and
roblastomas both in Sprague-Dawley X 10.000, 6,000, and 2,500 ppm, when
16# incidence of gliomas (oli-
txperiments studying the effects of the hloride (Table 17), vinyIidene chloride (Table 20), styrene oxide (Table 21L
(Table 23), benzene (Table 24), yl chloride (Table 26). f ( bove-mentioned compounds, wnors.
| ,
;
Maltoni et ai: Experimental Contributions
245
Conclusions and Discussion
In the reported experiments, two compounds, vinyl chloride and acrylonitrile, appeared to cause brain tumors, neuroblastomas and gliomas (oligodendrogliomas), respectively, when given by inhalation.
Such an effect is not seen with vinyl chloride at 500 ppm and below (Table 27) and with acrylonitrile at 10 ppm and below.
In Table^28 and 29 the overall incidence of brain tumors (different types and totals) in Sprague-Dawley rats following exposure, respectively, by inhalation and ingestion to different industrial compounds, without taking into account con centrations and duration and schedule of treatment, is presented.
From Table 28 it appears that when the level of dose and the type of tumor are not considered, the incidence of brain tumors may be "lowered" to borderline levels.
Such an "artifact" finding, in our opinion, is extremely important, and it stresses the point that, in epidemiological investigations tn humans, reference must always be made to defined types of tumors and to groups of individuals with the same level of exposure (homogeneous groups).
Our research in the field of carcinogenesis is now being extended to other ' industrial compounds.
Furthermore, in consideration of the higher responsiveness of embryos and newborn animals, we are now testing a series of compounds (including some of the ones considered in this report), by treating the breeders from the 12th day of pregnancy, and continuing the exposure of offsprings up to adult age.
References
1. Mancuso, T. F., E. M. Mac Farlane & J. D. Porterfield. 1955. The distribution of cancer mortality in Ohio. Am. J. PubL Health 45 (It
2. Mancuso. T. F. 1963. Tumors of the central nervous system. Industrial considerations. Act* Unio. Int. Contra. Cancrum 19:488-489.
3. Mancuso, T. F,, A. Ctocco & A. A. El-Attar. 1968. An epidemiological approach to the rubber industry. A study based on departmental experience; 1. Occup. Med. 10:213-231
A Mancuso. T. F. 1975. Epidemiological investigations of occupational cancers in the rubber industry, in The New Multinational Health Hazards. C. Levinson, Ed, pp. 80-136.1CF.
5. Maltoni, C,, G. Lefemine, P. Chieco & D. CarrEm. 1974. La cancerogenesi ambiemale e professionale: nuove prospective alia luce della cancerogenesi da cloruro di vinile. Gli Ospedali della Vita i :4-66.
6. Wagoner, J. K. 1974. Statement before the Subcommittee on the Environment of the US. Senate Commerce Committee.
7. Kuschner, M,, S. Laskin. R. T. Drew, V. Cappiello & N. Nelson. 1975. The inhalation carcinogenicity of alpha halo-ether 3. Life-time and limited period inhalation study with bis (chloromethyl) ether at 0.1 ppm. Arch. Environ. Health 30:73-77.
8. Maltonl C. & G. Lefemine. 1975. Carcinogenicity bioassays of vinyl chloride: Current results. Ann. N.Y. Acad. So. 246:195-218.
9. Maltonl C. 1977. Vinyl chloride carcinogenicity: An experimental model for car cinogenesis studies. In Origins of Human Cancer, pp. 119-146. Cold Spring Harbor Laboratory, N.Y.
10. Maltonl C, A. Ciliberti & V. Di Maio. 1977. Carcinogenicity bioassays on rats of acrylonitrile administered by inhalation and by ingestion. La Medibna dd Lavoro 60:401-411.
1L U.S. Department of Labor. 1978. Occupational exposure to acrylonitrile (vinyl cyanklL Proposed standard and notice of hearing Fed Regisl. 432586-2621.
OLI 6982
;<*
Tabu IS
Oveaall iNciDeNCi or Baain Tumoa* in Siaou-Oawlsy Rats. Foilowino thb Exraune bv Inhalation to Outwent Industalal
CONFOUNDS
Agent
Vinyl chloride
Vinylidcnc chloride
Dichloroethane
Acrylo* nitrile
miuiuis
No. at Sex Start
M 7K0 F 780 MF 1,560
M 180 I- ISO
MF 360 M 360 F 360 MF 720
M 120 F 120 MF 240
Tumor*
Neuroblastoma*
Ependymoma*
Glioma*
Meningioma*
Total
Average
Average
Average
Average
Average
Latency
latency
latency
Latency
Latency
Time
Time
Time
Time
Time
No. % (Weeks) No. % (Weeks) No. % (Weeks) No. % (Week*) No. % (weeks)
7 0.9 S 1.0 15 1.0
0 0 0 ___
0-- 0-- 0--
0 ___ 0-- 0--
77.0 74.1 75.5
___ -- ___
-- --
--
___ --
--
1 0.1 2 0.2 3 0.2
0 -----1 0.5 1 0.3
0-- 0-- 0--
0-- 0-- 0 ---
1230 995 107.3
95.0 95.0
--
--
"
--
-- --
6 OS 4 0.5 10 0.6
2 l.l 1 0.5 3 0.8
1 03 2 0.5 3 0.4
3 2.5 2 1.7 5 2.1
104 7 104.7 104.4
II 1.0 840 102.0
155.0 94.0 114.3
82.3 114.5 95.2
2 02 3 04 5 0.3
1 05 2 II 3 0.8
0-- 1 0.3 1 0.1
1 0.8 2 1.7 3 '?
113.0 89.7 99.0
127.0 116.0 119.7
-- 97.0 97.0
99.0 106.0 104 0
16 2.0 17 2.2 33 2.1
3 1.7 4 2.2 7 1.9
1 03 3 0.8 4 0.5
4 3.3 4 3.3 8 1.3
94.7 86.9 90.7
116 3 102.7 108.6
1550 95.0 110.0
86.5 II0S 98 5
i
I L 6 9 8 3
OLI 6984
Vinyl ' bride
Vinylidenc chloride
Dichloroclh*ne
Acrylo nitrile
0 0 0
0 0 0
1 0.S 2 It 3 0.8
0-- 1 03 1 01
1 08 2 1.7 3 1.2
127.0 116.0 119.7
--
97.0 97.0
99.0 106.0 104.0
3 1.7 4 2.2 7 1.9
1 0.3 3 0.8 4 0,5
4 3.3 4 3.3 3.3
116.3 102.7 108.6
155.0 95.0 110.0
86.5 110.5 98 5
Styrene
M 150 F ISO MF 300
0-- 0-- 0--
-- -- --
Propylene
M F MF
320 320 640
0-- 0-- 0--
-- --
Trichlorofluoromcihene
M F MF
180 >80 360
0-- 0-- 0--
-- -- --
Dtthlorodifluoromclhane
M F MF
180 180 360
0--
0-- 0--
-- -- --
Chloroa diOuoro$ muthiine
M F MF
120 120 240
0-- 0-- 0--
-- --
ConiroU
M 1.3X4
0--
--
F
1,412 . 0 --
*
MF 2,796
0--
--
0-- 0-- 0--
0-- 0-- 0--
0-- l 0.5 1 0,3
0-- 0 0--
0-- 1 0.8 1 0.4
3 02 4 0.3 7 0.2
*--
._
--
_
__
--
.....
103.0 103.0
_ _
--
,,
96.0 96.0
95.0 105.5 101.0
0_
1 07 1 03
0. 0 0--
2 1.1 1 05 3 0.8
4 2.2 2 l.l 6 1.7
2 1.7 0-- 2 08
13 0.9 8 0.6 21 07
,,
106.0 1060
_
-- --
129.5 750 111.3
102.5 93.5 99.5
78.5
78.5
118.5 813 104.3
2 13 3 20 5 1.7
0_
1 0.3 l Ol
1 0.5 3 1.7 4 1.1
0_
0-- 0--
l 0.8 2 1.7 3 1.2
10 07 9 0.6 19 07
1260 112.7 118.0
-- 1110 111.0
72.0 89.3 850
-- -- --
124.0 99.5 107.7
96.6 117.1 106.3
2 1.3 4 17 6 10
0-- I* 0.3 1 0.1
3 1.7 5 2.8 8 12
4 12 2 l.l 6 1.7
3 2.5 3 2.5 6 2.5
26 1.9 21 1.5 47 1.7
1260 1110 116.0
-- 111.0 111.0
1103 89.2 97.1
1025 93.5 99.5
93.7 98.1 960
107.4 101 3 104.6
1
iv * f
)
\
)
ffcinatourciiiifi l jirflli'iif nr i I t S
i*S\'b U . yf' i * , r -, vm4*m*mm*mmm***im*mm*m
1* i . ^ ' 9. 'J 4, iiliwiRiRR Rriin
o
H V0 00 U1
*
Tabu 29
Overall Inodencb or Bilain Tumors in Sfraoue-Dawlsv Rats Following Exposure av Inorstion to Dutkrent Industrial Comnunw
Agent
Turnon*
Ependymomas
Gliomas
Meningiomas
Total
Animali
Average Latency
Average Latency
Average latency
Average Latency
No. at
Time
Time
Time
Time
Sex Stan No. % (Weeks) No. % (Weeks) No. % (Weeks) No. % (Weeks)
Vinyl chloride
Vinylidene chloride
Acrylonitrile
Styrene
M F MiF
M F Mi F
M F M&F
M F MAF
MS MS 690
200 200 400
40 40 80
80 80 too
2 0.6 2 0.6 4 0.6
1 0.S 0-- 1 0.2
0-- 0-- 0--
0 1 12 1 06
103 5 90S 97.0
86.0 -- 86.0
--
--
-- 82.0 82.0
S 1.4 101.6 2 0.6 96.5 7 1.0 loot
1 0.5 0-- 1 0.2
80.0
--
80.0
0-- l 2.5 1 13
-- 430 430
1 1.2 106.0 0 -- -1 0.6 1060
1 0.3 2 0.6 3 04
120.0 65.0 83.3
8 2.1 6 1.7 14 2.0
104.4 84.0 95.6
2 1.0 116.0 4 2.0
1 OS 118.0
1 0.S
3 07 116.7 . J 1.2
0--
--
0 --*
0 --. --
0-- 1 2.5 1 13
99.5 118.0 103.2
--
43.0 43.0
1 1.2 90.0 4 3.0 124.7 S 3.1 117.8
2 2.5 3 6.2 7 44
98.0 116.2 111.0
.
OLI 6986
MV*
Vinyl chloride
M F MAF
Vinylidene chloride
M F MA F
Acrylonitrile
M F MAF
Styrene
M F MAF
.1MII
345 34$ 690
200 200 400
40 40 80
80 80 160
no. % (Wecki) No. % (Week!) No. $6 (Wecki) No. % (Weeks)
2 0.6 2 0.6 4 0.6
1 0.S 0-- 1 0.2
0 ___ 0-- 0 --
0 ___ 1 1.2 1 0.6
103.$ 90.5 97.0
86.0
___
86.0
_ ____
--
--
82.0 82.0
$ 1.4 1 2 0.6 7 1.0 100.1
1 0.S 0-- 1 0.2
800 --
80.0
0-- 1 2,5 1 1.3
___
43.0 43.0
1 1.2 106.0
0--
--
1 0.6 106.0
1 03 2 06 3 04
120.0 65.0 83.3
2 1.0 116.0
1 OS 118.0
3 07 116.7
0 __ --
0 ___ 0--
--
1 1.2 90.0
4 5.0 124.7 $ 3.1 117.8
8 2-3 6 1.7 14 10
104.4 84.0 95.6
4 2.0 1 0.5 5 1.2
99.5 118,0 103.2
0 1 2.5 1 1.3
43.0 43.0
2 2.5 5 62 7 44
98.0
116 2 1110
Stymie oxide
M F MAF
80 80 160
___ ___
__
----
0 ___
0_
0--
___
--
1 1.2 107.0 3 3.7 128.3 4 IS 123.0
1 1.2 3 3.7 4 2.5
107.0 128.3 123.0
Vinylidene fluoride
Trichloro ethylene
M F MAF
M F MAF
65 65 130
60 60 120
1.5
0.8
o_
o 0--
113.0
___
113.0
.
_
--
0_
1 1.5 116.0 1 0.8 1160
, 1.7 100.0
0 ___
___
1 00 1000
0 ___ 0-- 0--
0 ___ 1 1.7 l 0.8
-- ~ --
--
1080 108.0
1 1.5 1 1.5 2 1.5
l 1.7 1 1.7 2 1.7
SI 30 1160 114.5
100.0 108.0 104.0
Benzene
M F MAF
65 65 130
0 0 ___ 0--
___ ___
1 1.5 1570
0 ___
___
1 08 157.0
1 1.5 115.0 1 1.5 123.0 2 1.5 119.0
2 3.1 1 1.5 3 2.3
136.0 123.0 131.7
Asbestos
M 40 0 --
0--
--0
I
(Crocydolite) F
40 0 --
MAF 80
----
0-- 0--
--
0--
--
--
0 0
--
Polyvinyl chloride
M F MAF
40 40 80
..
_
----
0_ 0--
0--
--
--
0--
0-- 0--
-- -- --
0-- 0-- 0--
-- -- --
COnlrolxt
M F MAF
325 325 650
0.3 104.0 0.6 91.5 0.5 95.7
3 0.9 2 0.6 5' 08
1020 114.2 106.9
3 0.9 4 1.2 7 l.l
102.1 100.2 101.1
7 2.1 8 13 15 13
102.4 101.5 101.9
* No neuroblastoma* were found, t Olive oil
)