Document ByLBBOByVr4ev1zb0gepXjVz4
L Tomafis ef af
Humans
T.i/'lr 2 Confirm'd
Animals
Chemical or indus- Main type of ex-
trial process
posure"
Target organ
13 Cyelophospha- Medicinal mide
Bladder
i \
Main route of exposure*
p o . mjection
Animal Mouse
Rat
Tnrgpt organ Route ol cxpo'.im
Hemopoietic system. lung
Various sites Bladder* Mammary gland
Various sites
ip sc miechor
Po *P 'P
1V
14 Oiethylstilbes- Medicinal trol
Uterus, vagina
po
Mouse Mouse
Rat Hamster Squirrel monkey
Mammary Mammary, lymphore-
ticular testis vagina Mammary, hypophy-
sis' bladder Kidney
Uterine serosa
P 0. s c injection s
implantation Local s c implantation
S C injection, s r implantation
s c imo'afitation
IS. Hematite min- .Occupational Lung mg (? radon)
Inhalation
Mouse, hamster. Negative
guinea pig Rat Negative
Inhalation 11 s c injection
16 Isopropyl oils ^Occupational* Nasal cavity, lar- Inhalation ynx
17 Melphalan
Medicinal
Hemopoietic sys- p o . mjec- Mouse lem lion
Rat
18 Mustard gas .Occupational' Lung, larynx
Inhalation
Mouse
No adequate tests
Initiator
1
Lung, lymphosareo-
mas
Local
Skin 'P
'P
Lung Local mammary
inhalation i s c miecl'on
19. 2-Naphthylam- ^.Occupational* Bladder fne
Inhalation, skin, p o.
Hamster,
monkey Mouse Rat. rabbit
dog. Bladder
Liver, lung Inadequate
p0
s c inieclion p0
20 Nickel (nickel ^Occupational Nasal cavity, lung Inhalation retining)
21 N,W-Bis(2chloroethyl)2-naphthy-
lamme
Medicinal
22 Oxymetholone Medicinal
Bladder Liver
p0 po
Rat Mouse, rat
ster
Mouse, rat
ham-
Lung Local
Local
Mouse Rat
Lung Local
No adequate tests
Inhalation sc .in injeeho
i m implantalior
iP s c injection
23 Phenacelm
Medicinal
Kidney
Po
No adeq.uale tests1'
24 Phenytom
Medicinal
Lymphoreticular p o , injec- Mouse
tissues
tion
Lymphoreticular tis- P-O.. i p. sues
25 Soot, tars, and iJOccupa* oils Jjonatr. environmen-
tal
Lung, skin (scroturn)
Inhalation, skin
Mouse rabbi!
Skin
Topical
26 Vinyl ehlonde ."Octfupatfonat* Liver.
brain/ Inhalation,
tungr
skin
Mouse, rat
Lung liver, blood Inhalation vessels mammary, Zymbat gland, kidney
" The main types of exposures mentioned are those by which the association has been demonstrated, exposures olher than tho mentioned may also occur
* The mam routes of exposure given may not be the only ones by which such effects could occur
r Indicative evidence * The induction of tumors of the nasal cavities in rats given phenacehn has been reported recently (S Odashima, person communication, 1977)
9051572880 CANCER RESEARCH VOL
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u wv wi l^ii w vv w v/ y v* * vi t f v vrnumiUUiO
nary tumors in rats The causative agent in hematite mining was found and those lor which the data were judged
has not been identified, and the role ol radon is suspected inadequate forevaluation
Ferric oxide was'not carcinogenic in mice, guinea pigs, or
Of the 368 chemicals evaluated in Volumes i to 16 of the
hamsters'when given by inhalation or mtratracheally.
monographs, the 26 associated with carreer induction in
Correlations between human and animal data should be humans have been referred to previously For 221 of the
somewhat easier for the remaining 21 compounds, because remaining 342 (Table 3), some evidence of carcinogenicity in most of these cases a single identified chemical is in 1 or more animat species was found. It should be stressed
involved. One notable exception, however, is arsenic com that for these chemicals (marked with an asterisk) no
pounds Occupational exposure or exposure of the general attempt was made to distinguish between those for which
population to drinking water containing high levels of "strong evidence' and "weak evidence of carcinogenicity,
arsenic or to arsemc-containing drugs is associated with following the criteria discussed m the last part of this paper,
the occurrence of skin cancer, while lung cancer is also existed or those for which additional confirmatory carcino
associated with occupational exposure. No definite carci genicity studies are needed For the majority of these
nogenic effect has been observed in the available results chemicals, evidence of human exposure exists but no
from expenmental studies.
evaluation of the carcinogenic risk to humans was made,
For 5 of the remaining 20 compounds, namely, benzene, either because no epidemiological studies or case reports
chloramphenicol, isopropyl oil, oxymetholone, and phena- were available (205 compounds) or because the results
cetin, no adequate carcinogenicity tests were available for were inconclusive. (Some case reports were available for 7
evaluation at the time that the monographs were prepared compounds. BHC/lmdane. carbon tetrachloride, chloram However, recent unpublished results indicate that phena- bucil, dimethyl sulfate, iron dextran, tris(aziridinyl)-p-ben-
cetin is carcinogenic in rats (S. Odashtma, personal com zoquinone and tris(1-aziridinyl)phosphine sulfide. Results
munication, 1977). The other 15 compounds were carcino of sorrte epidemiological studies were available for 9
genic in at feast one, but mostly in more than one, animal compounds, amitrole. beryllium compounds, DDT. dieldnn.
species.
dimethylcarbamoy! chloride, isoniazid. lead salts, pheno-
Comparison between target organs in humans and ani barbital, N-phenyl-2-naphthylamme.)
mats confirms that the carcinogens have, in some cases, the
For the remaining 121 chemicals, the available studies
same organ specificity in humans as that in experimental were inadequate to make an evaluation of the presence or
animats In most cases, the chemicals were tested in more absence of a carcinogenic effect in animals or humans.
than one animal species, but the similarity in organ specific
ity may be limited to only one of the animal species tested The chances forstmtlar target organs are apparently greater f similar routes of exposure are used (Table 2). However,
Conclusions and Discussion For 26 chemicals (or industrial processes) ol the 368
chemicals that were found to be carcinogenic in both evaluated in the first 16 volumes of the IARC monographs,
humans and animals were carcinogenic in the latter also an evaluation was made ot the positive association between
when administered by routes different from the one by exposure and occurrence of cancer in humans (Table 2) In
which humans are exposed The target organs in animals these cases, the presence or absence of evidence o,a carci
are more often multiple than in humans.
nogenicity in test animals was not used in the formulation
The evaluation of the carcinogenic risk to humans of of the evaluations as is shown, for instance, for benzene
these 26 chemicals or processes was based on evidence and arsenic compounds One important lesson from these
provided by epidemiological studies or case reports, and human carcinogens >s that experimental evidence has in
experimental evidence of carcinogenicity was not used m some cases preceded human evidence, and a similar effect
the formulation of the evaluation For several chemicals in humans might have been predicted.
(aflatoxin, 4-aminobiphenyl, bis(chloromethyl) ether,dieth-
For 221 of the 368 chemicals evaluated in the 16 mono
ylstilbestrol, melphalan, mustard gas. and vinyl chloride), graph volumes, some evidence of carcinogenicity was
experimental evidence of carcinogenicity preceded human found in at least 1 experimental animal species (Table 3)
evidence and a similar effect in humans could have been Humans are or can be exposed to the majority of these
predicted The case of bis(chloromethyl) ether is slightly chemicals In some instances, results of epidemiological
different from the others The first observations in humans, studies or case reports were available but provided insuffi indicating an unusual clustering of lung cancer in occupa cient evidence on which to base an evaluation In most
tionally exposed workers, were made as early as 1962 (45, instances, however, epidemiological studies or case reports
46) Evidence ol a carcinogenic tffect in animals was first were nol available (the general scarcity ol epidemiological
published in 1968 and preceded the publication ol the hrst studies noted throughout the monograph jnogram must be
2 epidemiological studies, which appeared in 1973 (25)
stressed) In no case was an attempt made to interpret
Chemicals Carclnogenicto Experimental Animals. While animal data directly in terms ol human risk or in terms of
in 196B it was considered that fists of carcinogens should the degree ol carcinogenicity evidence provided by the
not be prepared without an m-depth evaluation of the expenmental data However, a large number ol food addi
available evidence, which differs both quantitatively and tives. pesticides, and herbicides have been reviewed tor
qualitatively from compound to compound, an attempt is their toxicity by national and international agencies, and for
now made to separate chemicals evaluated tn the first 16 a number of them the experimental evidence of carcino
volumes of the IARC monographs into those for which genicity was considered sufficient to issue specific regula
some evidence of carcinogenicity in experimental animals tions or recommendations (39. 47) Therefore, insofar as
april 197b
90S1573
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f
I
ii;
i
i
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{ \
RSV0033794
L. Toma/is el at
Table 3
List of chemica/s lor which there ts some evidence of carcmojemcify m experimental animals only or for which the oata were inadequate lor evaluation oI the presence or absence of carcinogenicity (IARC monographs. Volumes I to 16
For (ho 26 compounds evaluated as carcinogenic to hitmans, see Table 2
1 Acetamide'"
49 y-Butyrolaclone
2. Acridine orange
50 Cadmium acetate
3. Acrillavlnium chlo 51 Cadmium chloride*
tolgene" 97 2,5`Diarmriotoluene
(suitate)
138 Disultirum
139 Dithranol"
140 Dulcm.
189 Lead caibonjH; 190 Lead chromate
19t lead phosphate'
ride
52. Cadmium powder* 98 Diazepam
141 Endrtn
192 Lead subacelale'
4. Actinomyctns*
53. Cadmium sullate'
99 Diazomethane'
142 Eosin (disodium
193. Ledate
5. Adnamycm
54 Cadmium sulfide' tOO Dibenz(a,ft)acri-
salt)
194 Light green SF'
6 Aidrin
55. Calcium arsenate
dine*
143 Epichloro hydrin* 195 Lindane*
7. Amaranth
56 Calcium chromate* 101 D.benzfa./jacridine' 144 t-Epoxyethy|.3.4- 196 Luteoskyrin'
8. 5-Aminoaf**-
57 Canthandin*
102 Dibenz(a.h (anthra
epoxycyclo hex 197 Magenta*
naphthene
58 Carbaryl
cene*
ane' 198 Maleic hydrazide'
9. p-Ammoazoben-
59 Carbon tetrachlo 103 Dibenzo(c,g}carba- 145 3.4-Epoxy-6-melh- 199. Maneb
zene*
ride*
zole'
ylcyclohexylme- 200 Mannomustine (c
10 o-Aminoazotoluene'
60. Carmoisine 61 Catechol
104 Dtbenzo(/i.rst)penU aphsne*
thyl-3,4-epoxy-6-
hydrochloridel'
methyl carboxyl- 201 Medphatan
11 p-Aminobenzotc
62 Chlorambucil'
105 Dibenzo(a,e)pyrene*
ale'
202 Medroxyprogestei
acid
63 Chlorinated diben- 106. Dibenzo(a,/)
146 cfs-9.10-Epoxy-
one acetate'
12. 2-Amino-5-(5-nitro-
zodioxins
pyrene*
slearic acid
203 Merphalan-f
2-turyl)-1t3,4*
64 Chlormadinone
107 Dibenzo(a.i)pyrene* 147 Estradiol mustard* 204. Mestranot'
thiadiazote"
acetate'
108 Dibenzo(a,/)pyrene` 148 Ethinylestradiol*
205 Methoxychlor
13. 4-Amino-2-mlro-
65 Chlorobenzilate*
109 1,2-Dibromo-3-
149 Ethionamide'
206 2-Methytaziridine
phenol
66. Chloroform
chloropropane* 150 Ethylene dibrom- 207 Melhylazoxymett
14. Amttrole'
67. Chloropropham
110. Dibutylmtrosamine'
ide'
nol acetate'
15. Anitine
68. Chloroquine
111. o-Dichtorobenzene 151 Ethylene oxide
208 Methyl carbamate
16 Anthramlic acid
69 p-Chloro-o-tolui-
112. p-Oichlorobenze
152 Ethylene sulfide' 209 N-Methyt-AM-dm.
17. Apholate
dine (hydrochlo 113 3,3'-Dichlorobenzi- 153 Ethytenethiourea'
trosoaniline'
18. Aramite* 19 Arsenic trioxide
ride) 70. Cholesterol
dine* 114 Irans-Dichlorobu-
154 Ethyl `methane- 2J(J 4.4'-Methylenebis
sulfonate'
chloroanilme)'
20 Aurolhiogtucpse* 71. Chromic chromate*
tene
155 Ethyl Selenac
211. 4,4'-Methylenebis
21 Azaserme*
72. Chromium acetate 115. 3,3'-0ichloro-4,4'- 156 Ethyl Tellurac
methylamline)'
22. Aziridme"
73 Chrysene*
diamino-diphenyt 157 Elhynodiol diace- 212 4,4'-Methylened.-
23. 2-(l-Azirtdinyl)-
74 Chrysoidine*
ether'
tate'
anilme
ethanot'
75 C.l Disperse Yel 116. Dietdrin*
158 Evans blue'
213. Methyl iodide'
24. Aziridyl benzoqui-
low 3
117. Diepoxybutane'
159 Fast green FCF'
214 Methyl _ melha'
none*
76. Cmnamyl anthrani- 118 1,2-Diethylhydra-
160. Ferbam
Sullonate*
25 A20benzene*
late
zine'
161 2-(2-Formylhydra- 215 W-Methyl-W'-nilrc
26. Barium chromate 77_ Citrus red No 2'
119 Dtethylmtrosamine'
zmo)-4-(5-nitro-2-
N-nitrosoguam
27. Benz(a)acrrdine* 78. Copper
B-hy- 120 Diethyl sulfate'
turyl)thrazole*
dine'
28. Benzjc)acndine*
droxyquinolme
121, Digiycidyt resorci 162. Fusarenon-X
2'i6. Methyl red
29. Benzo(b)fluoran- 79 Coumarm*
nol ether
163 Glycidatdehyde'
217 Methyl Selenac
thene*
80 Cycasm*
122 Dihydrosafrote'
164 Glycidyl oleate
218 Methyllhiouracif
30. Benzo(/)f1uoran- 81 Cyclochlorotme*
123 Dimethisterone
165 Glycidyl stearate
219 Metronidazole'
thene*
82 2.4-D and esters
124 Dimethoxane*
166 Griseofulvm*
220 Mirex*
31. Benzo(a)pyrene* 83 Daunomycin*
125 3,3'-Dimethoxyben- 167 Guinea green B*
221 Mitomycin C'
32 Benzo(e)pyrene* 84. D i C Red No. 9
zidme*
168 Heptachlor
222. Monocrotaline'
33. Benzyl chloride* 85. Dichlorodiphenyldi- 126 p-Dimelhytammo- 169 Hexamethylphos- 223 Monuron*
34. Benzyl violet 4B*
chloroethane
azobenzene*
phoramtde*
224 5-(Morpholino-
35. Beryllium*
(DDD)
127. p-Dimethylamino- 170. Hycanlhone (mesy
methyl)-3-[(5-
36. Beryllium oxide* 86. 1,1-Dichtoro-2,2-
benzenediazo-so-
late)*
nilrofurfuryh-
37. Beryllium phos phate*
38. Beryllium sullate*
bis(p-chlorophenyljethylene (DDE)
dium sulfonate
171. Hydrazine*
128 lrans-2-((Dimethyla- 172. Hydroqumone
mino)methylami- ,, 173. 4-Hydroxyazoben-
dene)-amino]-7 oxazolidinone 225. 1-Naphthytamine
39. Beryl ore*
87. DDT*
noJ-5*[2-t5-nrtro-
zene
226. Native carrage.
40. BHC technical 88. Diacetylaminoazo-
2-fury|)vinyl)-
174 8-Hydroxyquinoltne
ans*
grades)* 41. Bis(i-azindinyl)-
toluene
1,3.4-oxadiazote* 175 Hydroxysenkirkine 227 Nickel carbonyl
89 AI.N-Diacclylbenzi- ' 129 3.3'-Dimethylbenzi- 176 liwtono! 1.2.3-
220 Nicknlnmnc'
moiptiOl'fiopho-.-
rime'
phino siilluli)'
HO Di.ill.ito'
rimo'
rrl)|iynmi>'
f.tO DmKitliylc.Kli.tiiioyl til lum (tnxli,m'
??0 Nn kill nxriln' ?30 Nu kcl pnwih-r1
42 Disfc lilotoaitliyl)
91 2,4 Oi.immo.uii'iolo
cliliriKk'*
1/11 iron xli-xtiio*
231 Nil k(>l Mill .ulliil
ether*
(sulfate)
131. 1,1-Dimelhylhydra- 179 Iron oxide
232 Nindazote'
43 1,2-Bis(chloro-
92 4,4'-Dinminodi-
zme*
100 Iron-sorbilol-citric 233 5 Nitronco-
melhoxy)ethane'
phenyl ether'
132 1,2-Dimethythydra-
acid complex
naptilticne'
44 1,4-Bis(chloro-
93 1,2-Diammo-4-ni-
zme*
181 tsatidme'
234 4-Nitrobiphanyl
methoxymethy!)-
trobenzene
133 Dimetbylmtrosa-
182 Isonicolimc acid 235 Nitroturaldehyd:
benzene*
94. 1,4-Diamino-2-ni-
mme'
hydrazide*
semicarbazon
45. Blue VRS'
trobenzene
134 Dimethyl sutlate*
183 Isopropyl alcohol 236 1-{(5-Nilro furfur.
46. Brilliant blue FCF* 95 2,6-Diammo-3-
135 Dmilrosopentame- 184 Isosafrole*
dene)aminoj ;
47. 1,4-Butanediol di-
(phenylazo)-pyn-
thylenetetramine 185 Jacobme
imidozoliomoi
methane-sulfo- '
dine (hydrochlo 136 1,4-Dioxane'
186 Lasiocarpine'
237 N-|4-(5 Nilro-2-
nale (Myleran)'
ride)
137. 2,4'-Diphenyldi-
167 Lead acetate*
furyt)-2-th'azo
4J8 /3-Bulyrolactone* 96 2,4-Diamino-
amme
188. Lead arsenate
acetamide'
90S1574
CANCER RESEARCH VC
RSV0033795
Evaluation of Carcinogenicity of Chemicals
Table 3 ~ConluMtrd
2JB Nitrogen mustard
(hydrochloride)*
239 NitrOqpn mustard
N-us Hit* (liydio-
chlondet* 40 Nurosoelhyturea*
H Nilrosomethylurea* 242 W-Nil roso-N-met hyI-
urethan* 243 Norethisterone*
244 Norethisterone ace*
tale*
245 Norethynodrel*
246 Norgestrel 247 Ochratoxin A 248 170-Oestradiol*
249 Oestriol 250. Oeslrone' 251. Oil orange SS` 252. Orange I* 253. Orange G 254. Oxazepam* 255 Oxyphenbutazone 256 Parasorbic acid* 257. Patulm*
258 Penicillic acid' 259 Phemcarbazide' 260 Phenobarbital si
dium'
261 Phenoxybeozarmne' 27g Propylttvouracir
262 Phenylbutazone 280 Pyrimethamine'
263. m-Phi'iiylrni'di-
?fi 1 p-Quinnim
.itiiuic (hydro 21!J (Juintozuite*
chloride)
2B3 Reserpine
264 p-Phenylenedt-
284 Resorcihot
amine (hydro 285 Relrorsme*
chloride)
2B6 Rhodamme B*
265. N-Phenyt-2-
287 Rhodamme 6G*
naphthylamine* 288 Riddellnne
268 Polychlorinated bi 289. Saccharated iron*
phenyls*
290 Satrole*
267 Ponceau MX*
291, Scarlet red
268 Ponceau 3B*
292 Selenium com
269 Ponceau SX
pounds
270 Potassium arsemte 293 Semicarbazide (hy
271 Potassium bi*(2-hy-
drochloride)*
droxyethyl)-di- 294 Senectphylline
thiocarbamate* 295. Senkirkme
272. Progesterone*
296. Sodium arsenate
273. Pronetalol hydro- 297. Sodium arsemte
chtoride*
298. Sodium dichromate
274. 1.3-Propanesul-
299 Sodium diethyldi-
tone*
thi ocarba mate
275 Propham
300 Sterigmatocystin*
276 /3-Propiolactone* 301 Slreptozoloctn*
277. n-Propyl carba 302 Strontium chro
mate*
mate*
278 Propylene oxide" 303. Styrene oxide
304 Succinic rinrio*
anhy-
rtif. Si n tan r
300 Sudan H*
307. Sudan ttl
308. Sudan brown RR
309 Sudan red 7B
310 Sunsel yellow FCF 311. 2.4.5-T and eslers
312 Tannic acid*
313 Terpene polychlon-
nates* 314. Tesloslerone*
315. Tetraelhyl & tetramethyl lead
316 Thioaceiamide*
317. 4,4'-Thioamline*
318. Thiouracil' 319 Thiourea*
320 Thiram 321. o-Toluidine (hydro
chloride)
322 Trichloroethylene* 323 Trichtorolrielhy-
lamtne hydro
chloride
324 Triethyler.u glycol diglycidyl ether*
325. Tris(aziridmyl)-p-
benzoqutnonc' 326 Tn'.(t-firintlinyl)-
litui'.plum- iixmIp
J27 fris(t-nziudlnyl)-
phosphme sullide*
328 2,4 6-Tris(1-aziridi-
ny!)-s-triazine" 329 1,2.3-Tris(ch!oro-
me1hoxy)-pro-
pane*
330 Tns(2-melhyt-1-
aziridinyl)phos-
phine oxide
331 Trypan blue* 332 Uracil mustard*
333 Urethan*
334 Vinyl cyclohexane
335 2.4-Xyiidine (hydro
chloride)
336 2,5-Xylidme (hydro-
chlonde)
337. Yellow AB
338 Yellow OB*
339 Zeclran
340 Zinc chromate hy
droxide*
341. Zmeb
342. Ziram
I
Asterisk, chemicals for which there is some evidence of carcinogenicity in experimental animals only (see also text, p 681).
food additives or chemical residues in food are concerned, the value of experimental results to predict a similar effect in humans has been accepted as valid.
The criteria used in the preparation of the draft mono graphs, in judging the adequacy of the data and in evaluat ing the carcinogenic risk of chemicals to humans, were first
fabltshed in 1971 and. with minor modifications, have ^een adopted by all the working groups whose delibera tions have resulted in the first 16 volumes of the IARC monograph senes Adherence to thts basic uniform back ground and maintenance of a certain rigidity in observing the rules set out in the preamble to the monographs permitted a relative uniformity of the evaluations formulated by the working groups
The growing success and overall acceptance of this program have certainly not prevented suggestions and criti cisms Criticisms mostly refer to the fact that, except for the few instances in which an association between exposure to a chemical and occurrence of cancer in humans has been clearly confirmed, the monographs do not give a clear indication as to whether exposure to a chemical does or does not represent a hazard to humans because no attempt was made to evaluate the potential human risk In most cases, in fact, the monographs only evaluate the carcino genic risk of chemicals to experimental animals without making any attempt to interpret the results in terms of a possible risk for humans.
It was for these reasons that an ad hoc working group, jointly called by IARC/WHO, was convened in October 1977 in Lyon to update and revise the criteria on which the carcinogenicity of chemicals to humans and/or experimen
tal animals is assessed and on which the evaluation of the
possible carcinogenic risk that they may represent for humans is made.
The report resulting from this meeting will appear as the "Preamble" of Volume 17 of the IARC monograph senes which is presently in preparation (38) and will replace the introductory section called "Background and Purpose of the JARC Program on the Evaluation of the Carcmoge c Risk of Chemicals to Man.' which appeared since 1971 with only minor modifications in all the 16 published monograph volumes. We would like to mention briefly here only the more significant changes that will henceforth influence the formulation of the evaluations, and the reader is referred to IARC Monograph. Volume 17. for the text m its entirety.
While it was recognized that no adequate criteria are presently available to interpret experimental data on carci nogenicity directly m terms of their carcinogenic potential to humans, it was also noted that extrapolations to a possible human risk can be. reasonably approximated by utiJizmg data from appropriate animal tests. These data, however, may represent different degrees of evidence, this drawback being mainly due to our present insufficient knowledge of the mechanisms of carcinogenesis "Strong evidence" of carcinogenicity is indicated by the unques tionable production of malignant tumors, white "weak evidence" of carcinogenicity reflects the qualitative and/or quantitative limitations of the experimental results of which a particular case could be. for instance, the induction solely from benign tumors in mice In the presence of ap propriate experimental carcinogenicity data and in the absence of adequate human data, it is reasonable to regard chemicals for which there ts "strong evidence" of carcino genicity as if they were carcinogenic to humans. Chemicals
APRIL 1978
3061575
883
F
L Tomatis et a!
for which the<e rs weak evidence of carcinogenicity in ex perimental ammals will, in general, require more experi
mental and epidemiological investigation. It was recognized that there are no acceptable methods
lor quantifying the possible errors in making an approxi mate quantitative evaluation o! human risk at some given exposure level on the basis of data that provide strong evidence of carcinogenicity in experimental animals The limited data available, however, suggest that such a rela tionship may exisl. at least within certain classes of carci nogenic chemicals, provided that account is taken of the nature of the chemical concerned and of the possible
ol the moncQUuhn Wiitiout fhov roirorfnc priifpsuonat dtivicc ,mrf sui't the monograph program Could no! have been implemented and continu
Or J Cooper and Or S 5<egei, Project Oncers ol the Nat-ona* Institute o* the United Stales we*e instrumental m initiating and mmnia.r active mln/rsi and support in ih*s program Wc would tWso tki io ti>nnk K E MrColnb ol SH* intnrnAtmnriJ unf Dr J R W.isvmt ol P*i twirnw*. tal Mutagen information Center. Oak. Ridge National laboratory Tor r> cHorls in providing data particularly on produchon and use ol chemic and on their mutagenic and teratogenic effects, and Dr. v Ponomarv
Dr T Kuroki. and Dr l Gnciutc tot their valuable contributions at monograph meetings
We also Thank D MioUon and 1 PelerschmiU (or assistance in bibliographical research C Partensky and E Ward lor technical and r
editing of Ihe monographs A Anderson MJ Ghess, end R Johnson secretarial help and R Johnson l Kitchen and E Perez lor assistance the preparation of this manuscript
physiological, pharmacological, and toxicological differ
ences between (he test animals and humans
References
More consideration than in the past is also given 1o indirect tests, most of which do not have the production of neoplasms in ammals as the end point and are generally referred to as "short-term" tests. These lests are proposed to be used, (a) for the prediction of potential carcinogenic ity when other carcinogenicity data are absent, (b) to contribute to the setting of priorities for chemicals to be tested in animals, (c) for the identification of active frac tions from complex mixtures containing carcinogens, (d) lor the identification of active metabolites of cacmogens in human body fluids, and (e) to help elucidate mechanisms of chemical carcinogenesis
The last section ot the monographs, which was originally headed "Comments on Oata Reported and Evaluation," and comprised 2 subheadings. 1 for experimental data and 1 for human data, will now be called "Summary of Oata Reported and Evaluation", it will have 3 sections, > e . a summary of experimental data, a summary of the human data, and the evaluation The evaluation section will lake into consideration all ol the data in the monograph, partic ularly the summarized information on ammals and humans
The revised criteria for the evaluation of the carcinogenic risk of chemicals to humans have already been applied by the IARC working group that finalized the monographs scheduled to appear as Volume 17, which considers some W-nitroso compounds (38)
By applying the new criteria lor the evaluation of the carcinogenicity of chemicals as they are described in the new preamble to the monographs, as well as acquiring further carcinogenicity and related data on chemicals and new knowledge on the mechanisms of carcinogenicity as it may become available, we hope that in the absence of epidemiological data a more clear distinction can be made between chemicals for which there is or is not evidence ol a possible carcinogenic effect in humans
We hope that in this way the cnncal analysis ol the experimental and lnmi.ui data nntl Ihe ensuing ovnlualinns ol onvuonnu'iilal <liriiiii .il'. will ni,ik<> lullin' IAIU'. mono graphs more usolul in assisting national and international authorities <n lorniiil.itiiuj deusions concerning preventive measures.
Acknowledgments
To list all the 177 investigators irom Pie 24 countries who have paritcpaled in and contributed to the IARC monograph program ts impossible Although this article retlecls our personal views and opinions, we express our deep gratitude to alt the individuals who participated in fhe preparation
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