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British Journal Of Industrial Medicine 1986;43:68569I
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An update of mortality among chemical workers'
exposed to benzene
G G BOND, E A M c L A R E N . C L B A L D W I N , R R COOK From Daw Chemicol IISA. Epidemiology. H & ES. Midland, Michigan 48674. U S A
4' . /
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ABSTRACT Mortality was updated to the end of l9e2 for 594 employees cxposcd to benzene who had been studied previously and for an additional 362 exposed workers not studied previously.
Cause specific mortality comparisons were made using United States white male, age, and calendar
year adjusted rates. Total mortality was observed to have k e n significantly k l o w expectation, and this was particularly evident for deaths from accidental cau3cs. Mortality from skin cancer was significantly raised, although there were no unusual or common characteristics among the affccted individuals which would suggest a link with exposure to benzene. A non-significant excess of t d deaths from leukaemia was noted based on four observed cases; however, all four were myelogenous leukaemias and this represented a significant excess in that subcategory. These and other deaths of possible interest are reviewed in detail. Analyses by work area, duration of exposure, and cumulative
dose index did not show patterns suggestive of a causal association between exposure to benzene and any particular cause of death.
There is a large amount of evidence to support the hypo&& that acute myelocytic leukaemia may be a
latent effect of overexposure to benzene' (B D Gold-
stein, unpublished data). Data to support increased
risks of other types of leukaemia or other cancers have
'been nponed, but arc in nced of further evaluation'
(0Wong, unpublished data). The exact shape of the
dose response curve for the knrcne kukaemia asociation is unknown and has k e n the source for spculation and controveny.'" One of the few studies
which has been relied on for risk assessment was reported by Ott et al in 1978.' They followed 594
Dow, Michigan Division. cmployecr potentially exposed in any of three production a m using k n m e . Two deaths from leukaemia were observed compared with one expected to the end of 1973. Afler excluding cohort members with other hazardous exposure, they observed OM death from leukaunia against 0.9 expected. A third subject died of bilateral
bronchopneumonia but had myeloblastic kukaemia listed on the death o c r t i b t c under "other significant
conditions."This death was coded to pneumonia consistent with the rules follomd by the World Health
Organisation.The present study updates the mortality experience of that cohort of 594 with an additional
nine years of follow up to the end of 1982, and
includes 362 exposed employes not studied originally.
MctboQrod matedab
A detailed description of the chlorobcnzol, alkyl k n =ne, and ethyl allulose operations in which thex employees had potential exposure to benzene was given by 011er d 6That reponalso should be consulted for summariesof industrial hygiene measurements used in exposurc classification, and the methods by which the cohort was identified.
In brief, 594 employas were identified from annual census lists aa having worked for one month or longer ktwecn 1938 and 1970 at job, of interest in the three production areas. For the pmcnt study, the ansus lists w m consultcd again. This included a review of monthly census liru availabk beginning in 1965. These had not been used for the original study. An additional 228 employees who met the cohort
definition of Ott cr aP were identified by this rc-vl.ew
and are included in the present investigation. Monthly CCIISUS liru from 1970to 1978 wm consultcd to W r tain another 134 employees potentially exposed aner the closing dnrc of the original study. Thus the present study reports mortality among 956 employas.
All job assignments icvolving potential exposure to benzene to the end of 1978 were coded and considered
685
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686
for exposure classiftation. Each job entry was assigned one of four exposure intensity levels (very low, low, moderate, and high) b a d on availabk industrial hygiene monitoring data.All jobsheld aner 1972 were classified as either low or very low exposure.
A cumulative dose index was calculated for each cohon member by multiplying the representative TWA value for each intensity level by the number of days exposed at each kvel, and dividing by 30.41
dayslmonth to yield ppm months. As in the original
paper of 011 cf u I ,t~he 'IWA value of I ppm was used for the very low level, 5 ppm for low level. 17 ppm for moderate kvel, and 30 ppm for high level.
Follow UP of the cohort for vital statu determination was done ruing company records, the camings and benefits records of the Social Security
Adminisvation to the end of 1979, and the National Death Index to the end of 1982. Death certificates were obtained and were d e d according to the Inter-
national Classification of Di- (ICD) NICS in
effect at the time of death by a nosologist experienced in multiple rcvision coding. Deaths were then tabulated by cause for analysis using the categories of the Sth ICD revision.
Analysa were carried out by production a m , duration of exposure, a d by cumulative dose index. Employes may have contributed penon-years ar.d
deaths to several categories. Allowance was made for a pouibk latency period by lagging uposurcs IS yean. Expected d a b were calculated by the indirect method ruing United S U t a white mak mortality rates via an updated venion of the hionson p m gramme (USDR 58).' S W r d i s a i mortality ratios
(SMRs) w m alculated u the ntio of otmmed to
expected deaths multiplied by 100, and Fisher's exact 95% confidence Limits a b u t the point cstimam' were computed wing thc programmer of Rothman and Boicc.p Examination of m d s across SMRs wu done
using a zz trmd (at with one degree of f d o m as
outlined by B d o w CI d.Io Previous studies at this plant had identified em-
ployas with p u t exporun to mmic," ubestos," or high levels of vinyl chloride1' u possibly k i n g at
Bond, M c h t e n . Baldwin. Cook
incmstJ risk for sew XI malignancia. Analyses were made both including and excluding those employees from the present cohort.
6
RcrPlb
Table I shows the vital and employment rtatus distribution of the cohort on 31 Dccember 1982. Follow up wes 98.4% complete; the I f employees lost to follow up were withdrawn from the life table on the date they wen last known to have been alive. A total of 225 deathr was identified, 25 of which were among the 68 employes who also had been exposed to askstos, .
arsenic or vinyl chloride. Death certificates were obtained for all but one (0.4%) of the decedents; this death of unknown cause was included in the totals for analysis but was not allocated to any cause specific
category.
The distribution of employees by period 6f first
exposure and duration of exposure is pmcnted in
table 2. The median year of first exposure was 1948,
and 784% of cohort rnanben were first exposed at least I5 years before the closing date of the study. The mean duration of exposure was 7.0 yean (median =
2.6). The 936 employees contributed a total of 24571
penon yean, for an average follow up of 25.7 years.
Theaverage age at entry into follow up was 31.0yean.
Table 3 presents the dislribution ofcohort members by exposure intensity level, and within each level by year of first exposure and duration of exposure. Improvements in exposure conditions over time and job mobility by employas resulted in most having been exposed at more than one intensity level. Nearly a quarter (229 subjects) of the cohort members were exposed in jobs categorid u 30 ppm l W A benzene exposure, and nearly a third (311) were exposed in jobs categorixd as 17 ppm TWA.
Table 4 shows the overall mortality comparisons for rlated causa of death. The all causes SMR for this cohort wu 84 (or 83 if the arsenic, asbestos, and vinyl chloride exposed subset is excluded). This rcprcsented a significant deficit m m M d with expectation but was consistent with !';e general pattern of lower mortality among WC~IO~CU from this plant." A
'
i
9% 888
IW I92
n3 146
15s 13s
3m31
31s 6J
246 233
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An updote of mortality am- chemical workers eXpaKd lo k e n e
- 687
held lrved opcntor orrigmenu with potentid high
level ~ Z U Wexposure until he ntired in 1962. His
atimrrsd career dosap was 4211 ppm m o n t h He
died aged 80 of myclomonocytic kukrmu'r; no nee
row wu prfonned. The i n t m r l bttwsm the ontet
1w
Ip10-19
1930-SP 196069
6 39 IM It1 35 45 72 53
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37 55 41 76 3x U do 4
137 3Sl
141 I89
of d h U 8nd d C d l W B I -nod to hrvc kta two
months.
Cuc number S w u not included in the originalOtt cohort. He began work with thecompany in 1928and
19mn
46 74 I8 0 I38 worked for one month in an 8 r u of potmthl ancnic
Told 265 333 ZW IS 936 exporurr before moving to chlombrnzol wherc he
worked flnt u an oprotor then u 8 thin forunm in
jobs clurifkd 01 low or very low benotm exporurr
until hi8 rrtirrmcnt in 1952. His estimatedcareer dor-
age was 343 ppm months. He did in I967 a p d 80 of
significant cxccu w u observed for skin caner bued acute myelomout kukacmia.
on four o k r v d deaths. A substantial and significant As w u tnw for the three deaths from kukocmia
& k i t was observd for rhc cotegory of rcciQnul obsewal by 011 et a/, both the new k u k u m i u had
deaths. No other significant m u l b wrc found for thc the potential for unquantifisd brief. but potentidly
other 54 causa of death evrlurtaj.
relatively high, exporuru to bcnzrne. In the alkyl btn-
Four deaths were OMfrom kukumio. m c a r a , kntmekwlswm marunduhigh as283
resulting in a non-significant QCCU for this ategoy. ppm in some u m p k in ethyl dlukme, u hi& u 937
The QLC summaries for h e x four dab lad for P pprn. Therefore. aution must bt cxcrcirad whm
Anh case clouifkd to pneumonia u1given in tabk 5. interpreting the cumulative do= indica.
Cuc n u m b 1-3
o r i g i d l y rcpomi by 011et There wu 8 non-rignifkant CXCCII of deaths
a/.* Cuc number 4 died in 1980 rRn tbe original OMin theategory of o h and unrpecitidd a n -
foilow ended. This mur began work at the oom- om.A micW of the deathccrtiAcltedirgntma for the
p n y in 1943 u an o p n t o r in S a m fabriation. seven'Rr
individuals did not show 8 mmmon
shortly thtrrrRcrhcmovad to alkyl knzlcntw&rc he tumour type nor any that were of lymphtic tirrw.
.
nuVaY
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1940 1910-9
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6aa Bond. M c h e n . BCJdwin. Cook
l2S 268.6 J9 31-7 2 1-11
13 15.1 0 1-3 3 2.8 7 44 0 1.7 0 1.1 2 3.0 20 19.1 0 0.8 ia 18.1 0 03 4 1.0
3 3.2 0 0-3 I 1.5 I 1.4
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7-5 82- I39 13401
46-147 0-284
22-3 I 3
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0-335 8-24 I 64-162
Mi
59-I 57 0-1230 loel024 I P-274 0-1130 2-37 I 2-39a 0-3699
1-328 0-3689
22-657 0-527
J24 2429 7e3w
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U-1151
70-101
4 sI43 13-UO 22-Id0 6-n *a6
200 242.3 49 499.2
2 I4
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6 4.4 0 1.J 0 1.0 2 2.7 14 17.2 0 0-8 I 3 16-3 0 0-2 4 0.9 2 24 0 0.3 0 I .4 I 1-3 00 I I4 0 0.1
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0 0.6 3 1.9 I 1.2 1 3.4 4 3.4 I 06 I06 121.4 I I 13.9
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2-Ma 0-3689
26122 0-615
3341 24 8WU
32-301
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71-106
40-142 14435 2sI77 64 49-149
,
In addition to the death, from rplutk and pmi- dassikd 8s potentially uposcd to several different aous anaemia (omuch) obsemd by 011er d,'OM levelsof benzeneincluding hi& until his n t i m c n t in o t h e r d a t h o o c u n s d f r o m ~ o f M o o d o r b l o o d 1965. His atimated aeoct dose was 6027 ppm
forming hut. This mm was h i d in 1923 and month. He dicd in 1980 a@ 80 of myelofibrosis.
w o r k d in many diffmt pbr indudin#an area of 'Ibe analysis of morulity in the total cohort was potential ancnic cxpowrr until 1939wkn hc s t t k d carrid out dowing for a IS year minimum latency into various opcntot p b r in alkyl benzene. He was &ad. This effeaively m o v e d tttc-. 5nt cxposcd
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alter 1967 fmm the rarlydr.Tbc mortality pttrm, obwmd for tho chloroknroi urd ethyl a ~ o e
dauibcd above wem not rltucd, rlthougb aome Of UIUI.
the caw cpscific SMRa were W rli#htly.
Table7ptacntr ObwrVed lad expaxed dacha fmm
Morulity results by work ua uc prrwatcd in rllanccricombid by yara ofexporuemd~nmvd
table 6. Some mrploycu worked in rnultfpk mu, s i n e 6nt exposure. Morulity w u romewhrtm i din
therefore they m y be countai more thrn once in t& thc period from IS to 19 yan after &tt upoj~n;
table.Totalmortalitywuoonristcntlyblow expactsd however, it wu h @ y indcpadcnt of duntion of
.. - lewis t a w the three work uaa. Although tbac mpo8urc.
were no statistially dgnif&antrim by work area, Tabk 8 show the resultsof dose nrponae analyses
marginal ex-
of skin cancer were o k m d only for r c W aw of dah ategoria U y x a wrc
for the alkyl kntcnc md ethyl Odlulors a m & lad mrdcbyflntIr~ngexpoturracroyeur,mdtbcn15
ex- lymphopoieticanccr wuobumd only forthe y a n to allow for tbe porribk e x p d o n of a latency
alkyl benome a m . A slight mcua of lung oocctWU period. Duntion of expoaure is m important corn-
obscmed among t h a who worked in ethyl c d l b , poncnt of m y cumulrtive dorc index md is ruongiy
w b e m desciu of this cancer wae okcrred for tk conclrtai with survival. Failure to lag expoaura to
other two production arcas. Smrll cxassa in tbc a t - compcnvtc for thi8 m y rudt in miuing 8 d o e
.. . e p r y of cancer of other and uupiikd ata wtlt =pone relation. There were no signilkant mortality
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690
Tablo 8 Morrdfty -y
expMvrtt
by esthrotrd &atlw
Bond. M c h r e n . Baldwin, Cook
dose of benzm expwnre. exrludhg employees with competing
All aua (001-9W) (w99 ppm moorha
~999ppmmonlh lomppnmoothr Toul
All a- (140-m))
0499
115.' 43 42 30
27
IS14 35.2 55.6 212.3
30.0
7.3 11.9 499.2
9-7 2-5 4. I 163
0.6 0.1 0.2 0.9
39 07 1.1 68
1.2 03 0.4 1.9
746 17.9 21.9
1214
76 122 76 83.
90
I.S-0. 92 100
62 204 49 Bo
--6763
441
-133
ta3 12s
-I67
uo
I58
sa
123 83 87
IS yra?s
Oh
Ios
33 17
165
17
9 7 43
8 4 I 13
4 0 0 4
3 0 2 5
2 0
3
53
21 IJ 89
~~
GP SMR
I 174 25.7
374
180.5
09
129
72 91
25.0 I08 -5 7. I s9 0 4 84
39-I I10
8-6 1.0 3.0 13.S
04 0-I 0. I 0.6
-2.3 132
0.5
b,0.7 214
3.5 142
-0.9 222
0.2
0.3 333 I 4 214
62.6 13.7
Ian5
Dl 75
%a3 92
trends for m y awe of deatb miurted. Oddly enough, mortrlity from awed awes w u somewhat mired among those c x p o d from u)o to 9!l9 pprn months. AU four &in ~ l l c mwm o k n d to have km in the lowst dose awry.
Dhrrk.
cxpoctcd. Taken together with the two deaths from
kukrrmir previously reported for this cohort, the
total still doer not represent a statistically significant
-CXCCII of toul k u k d a . It docs represent, however,
a riguiffant excess of mortality from myelogenous kuhmia(4obrcnsdHnur0.9expected;p 0911)
-whcn mortality data compikd from the Surveillance,
Epidemiology and End Ruulu programme arc used
as a compujlon.t*
t
'lk datb from myelofibrosis is intcruting since
thisconditionis bciieved to represent a primary over-
growth of a ~ V fibCroblastic a l l line, analogous to
mydomo~
I' There have been stvera~
nporuof myelotlbrorir among anployetr with alleg-
edly lmvy bcllEcM exporun (B D Goldstein.
unpublisheddata). Among thedeathsfrom other lym-
phoreciculu ancer wu one multipk myeloma. This
did not rtprrrcnt an ex- over expaxation and is
nocrbk only because Dscou& er d suggested a link
be- thh condition m n d knomc.'
An unexpected finding w u a signrkanr CAW of
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An update of mortalily m o n g chemical workers exposed to benzene
691
mortality from skin cancer, bared on four o&urvod a small number of events, ampcting exposures to
cases. A review of the death artiflater : h o d that other @tentially hazardour materiais, and the unar- '
thm of the four were malignant melanomas, the tain contribution of unquantified brief exposum.
fourth was described BI a squamous a l l arcinoma.
There were no unusual or common charactcrirtia We gratefully acknowledge the technical support
among the affected individual's work historia that received from Dr M Gerald Ott, Karen Wymcr, Jan-
would suggest a link with benunc or any other work- ice Cartmill, and Bernard h i c h . Angie Grzcgomyk
place exposum. All four were classified into the low- typed the manuscript.
a t cumulative dose category. %our repom of
mortality among benzene exposed workers have not
noted exass skin canctr, or more specifically mela-
noma, and thus its finding here may represent ~JI
isolated or chance occurrence'-* (B D Goldstein and
0 Wong. unpublished data).
Mortality from accidental causes of death was
obscerved to have becn substantially below
expectation. even by indirect comparison with other
employees from this
There is no availobk
explanation for this deficit but a@n it may rcprrrcnt
a chance arurrena.
Analysis by work area duration of exposure, and
cumulative dose index did not show p t t r n u sug-
gcstivc of a causal d a t i o n ktwscn expourn! to
b e m e and any p o r t i ~ ual ~t g o r y of dath. Three
of the four patimuwith kukaemir, OM with multipk
myclomqmd one with mydoflbrosisworkod in alkyl
benzcne. This may indicate that lorn additional CQ-
factor may be imponant in the actioloa of that
deaths. Other materids prwcnt in this work UQ
included ethylknzmc, divinylknom, tolume,
xylene, isopropyl knamc, styrene, dbopropyl bcn-
m e , a d alpha-methyl styme.
I Askoy reccntly suggested a link between exposure
to benzene and lungc a w . * We found no evidcucz to
support such an auocirtion in out study. LungM c c r
was not found to be excessive in tbe toul cobonor in
I the cohort krs exclusion^ (13 OM@ntt 16.3
expected), nor was thm a tmd of irrraring lung
a n a r risk with incrusing exposure. Tbt s t d y hd
95% p o w to d e w I twofold ririr d l u g
with a one uilcd t a t 8d dph8 = 005, rad 57%
power to detect a om and a half-fold risk.
Although this study provida supper\ lor tbe UIO.
ciation k t w a n exposure to
md acute
myelogenous kukaanir report& by otkra' (B D
Goldstein), wen1 factors obmplhte w of tkrc
data for risk aucsrmmt. Thcrtincludetheprobkmof
,