Document B8dDgBxp2Kgr686BYqow2Ozdj
Apr-14-01 12:21pm Frorn-
Acute m y e W leukemia (Ah&) is characrcJized by
acquin=d. nonraadamclonal ~hromosorrreahmmalities,
which have provedto be clinicaliy and biologicallyim-
pomar sin& they provide diagrrostic. prognosck, e t b
krgk and pahogen& infans;irau (1.2). soarr?experi-
--'Imcatunsreadl isffceurdeinest
indicate Qat different exposures m y types of clonal chmmomme abnomtali-
rk(3-a Punbermom, AML followingd o orckm-
0cher;rPy differscytogenetically from de nova AML (6,
7).The ptrzms fCtrcIom1ChrWMPa b n m i i u e s ia
agenu have been associared with total or partial losses of c h m ~ r r m e5s and 7 add ddcrionsaf the short arms of chmomnxs 3 and 12. WhmM topairomernse-lr inhibitMEhave been linked to srruciuralrewrangemtsof chrcrmosomebands 1lq23 and 21q22&9). In addition.
id peripheral lymphocytes of healthy workers exposed to
high coTlccntrariOnr of bcnscne, Qsedependenr griw
(mainly trisomy)of ckom~somz8 (10)add deleubmof chromosomes 5 and 7 C11) havebeen found.
Known risk factors for AML include radio- and
chemorherapy. bcnzeneexposunk and smoking (12). In
addition. exposure to o t k r organic solvznrs (13). ex-
I Apr-18-01 12:21pm Fron-
T-415 P.03/11 F-465 Afhher a1
mmdy low fiequoncy tlectrwlagnutic fields (ElMF) (14-18), hair dyes (1!+21), pesticides (22). petroleum products and exhusr gases (23). dmalbomt viruses
(241, and fcmuy work (25) have beenindicated as risk factors,albeit with confiiainglesults(12,26).
stlldies ofsu&ysted o c c u ~ n arilskfacms far spccific subtypes of AML, as defined by rnorpbbgy br
karyotype, have aoo1been consistent. Exposure was not associami wirh any specific marphology in one study (271,urherw- others have indicated i m a s e d risks for
acute myelomonocyticlcukemja &r benzene (28) and peaicide (29) exposum. i n d r j s k for acute promy-
Czlocyticleukemia in elecuicians(30).and a possibleassocktion between exposure tosolvents.insecdcides,ot petroleumproducts and erythroleukemia(31). With regard IO c l m l chromosormalmormalirics, in some studies, AML.patients ~xpaPodu)sdwms 01 pemicides (31-
33)or 'chemicalu" (27.34) had a kighm proportion of
clomal chqnc&ameabnonnalitie (cspacially cornpbte
or p i a l lossdchnomosorae5 or 7. aod trisomy 8). but not in orhas (I d35.36).It has alsobeen ruggesredthat
AML io ~ s o c i a rwi i~rh previous roxic occupational exposam hasa woise prognosis and qmsenti a disdnct
clirlicd.as milas qtogenezic,entity (32). Limt is h o w n abaur rhc effccr modificarion of tx-
posunby a&, genckr, and smoking in AML.However,
sidlcrcl al(373ObscIvGd 86 exp6snrc-nspmstbehvcen SmQkmg andrisk for AML only fcx subjecrs above tbe age of 60years at &e ofdiagnosh.
The pmwt study was unlnaJreato expkue prevaient apcwrcs. such BS organic sclvents, ELhdF,and la& dyes. suggcsrsdas risk hctonin preview studies wirh regardto o v d l risk for AML M m w , other objec-
tives were IO study chararmisticclonal cimmosorneabnormalities@ markers of exposure, diffemtial risksfor mctrpldogicaisubtypes,and effecc moditicafi011 by age.
$onflex,a d ~ ~ n ~ k i ~ g .
cases
Our study is based on a scsjes of 372 umse~udvecases
d Ah&. d i a p o d h e m 1976 and 1993;the sub$cts were at least 20 years of age when cytogenetically dvestigaredat &e Dcpartmant of Clinical Generics,Ludd, which pelfcmls all cytegenctjcanalysesiaswcheanswedcn.AU referralsfor such analyses are ma& wirhh the pubiic Wdr system. "%e hatoIogy depar&m~81 he Lund Univemiry Huspital and at thc n&y b ~ p i t din Helsingbcug, thmughwt &e study paioti, included cytogCnetic Sfnalysesas a routine in the diagnmliccrtIrmtioxl of hemamlogical dgnancies, lodicading that the coverage of incidem cases is mclsf complete far rhese catchmcat areas (Lund-Helhgbmg). Intmkw mformah a was obtajntdfbr333 caas(9096) (table 1). The non-
parcicipadng caseswcrc OW(median age 68years] and
fLum cdknwamm 09%). The medical meo& for eachcase werereviewedby
1 Of3 Jmnadogisn(38)."hediagnosesw m based on tbc moiphoiogical hnd clinical findings present 81 the time 61the CyIPgeneric investigation. The m o ~ o g i ca1 subqpcs according to the French-Amerjcan-IBritkh FAB) cl;rsPiflcacianwe= as follows: miaimally M i x enrfawd (MO)1 case, myeloblastic without melmUim
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a
Referents
Statistics Swedcn seleaed 3 referents foreach case.
-----Imatched wich e p e c t to gender, year ofbinh. and CyIun-
ty of living fmnthesmdy popukion (souchemS w a n )
within the calends year in which each case was diag-
* nosed. Ode referent in each matched set was randomly
selected 10 be interviewed.Whcn referenrsor h k eext-
I
of kin could not k inrwizwud, orherreferems from rhe match& set were sekcced M t o g e t k 351referentswrra ineluded in the study (parriciphn rate 72%) (ubkI). The nonparticipatingrekrenrs wert alder (median age 68 years) and mmc o m women (60%).
The s ~ b j e a sw r c r o t r o s w v d y cnrollcd in rhe study and conlacted with a letter describing the purpasc
484 Scand J work Envimn Hegllh 2o00,df26,no 6
dtht study and rhcmain question9 to be addmseddur-
ing the inmiew. A life-hhg aecupati&nalbtrmy was
&mined during chc Mod 1995-1997 in a
rmuculred rekpbne 'mrview made by 1 of3 occupa-
ticmadheal* nurSCS who were a w m of thecase-refemt
st~hlli.The histmy inc!eW all jobs held far at h r 1
ycar. k l d i g w m h k ciepamm, d nameofcom-
pany. No specific e s r p o s ~were asked fclr ia &e her-
view, bur follow-up questions w e triggered
iag cbzapp.iicacionufpesdeidesinwork as ilgardeRuor
horricuhrisr, lumberjack, zdway w o r k (track main-
renancc), f m m , oraamhmri;cype of WrgQ inwoslr,as
a driver or un a m d m t ship;handlingofc y t o d c s in
work as a rmmz; and working I a mea counter in work
aa ashop Wpm oc shop assismm. Infbrrrmrionon extra
jobti held f a at least 1 year wns collmtcd in tbe same
way as for the regnlarjob.
Tbe following hobby rriviries were explicitly in-
quid abom:motor repair, mi& pluuing withoil. fur-
nimm renovattoa,CcuJs~tionbfmOderkich%,animal
h d i a g . hrmring, wd gardening. Follow-up questions
were asked & h u rxrivity periodand average hours per
week spcnr in ihbe aaivity. A follow-upquesrionOII reg-
ular pcslicide use was triggered by gnrdsniag as a hob-
by.Furthennore, qucsrions WCIS asked abouc awar hair
dye UK.and smoking habits. Tlze medical histmy pre-
ceding&a rim of the casediagnosis iacluded quesrianr
&our radiotherapy. chtmtttewy,and ct-
wim
imp.
lf rhz 3ubjjcct was deceasedMtaa ill to penicipe, a
nexc-&kin was selsred in the fdhar;lg orda:spusc,
parenr., siilmg. and cbild. Infomciw hadLDbe OMIiOcd
fmrhtnext-&-kin more oftzn for cases rhan fm mfer-
e m (tahle 1). The proporriOn of nexrsf-kin interviews
increased as the age of thc subjtccs increased (eg. next-
of kin imerviews were used & 933% of the cases and
23.5% ofthe refmnrs o mthan60y%Wsof agck S p -
es and children were rbz most frrquently interviewed
amng the next-&kin abath thecases (48% and 36%,
respectively) and ehe r e f m r s (27% and 6396,rcspzc-
tively).
Exposure assessmerlt
Exposure aSS2SSm2ntwas pesfwmcd by 1of 3 OCCUpational hygienists, CUI tho basis of the suuctured relep b inaetviewsmadeby the ocqat-malhedrhnurs-
es. Tbe occuparional hygienists werc U M W ~of the casI?-rcfemntstatus, The ssesfllocncs For all cases,and
for rb ccurespondingrefeenu, were rtsrrictcdUI erposure periodsof at least 1 year duringthe 20 years before [he diagnwis of the case. All ccdings w p e supervised by double-checks petformed by one of the hygienists
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Apr-14-01 12:23pm From-
Albin QIai
Exposure assessments were performed for estab- judged from coinparisonswith rhe medical recordsavail-
lished, and suggcsred.cccupaficnaland leisure-timerisk ableforthe cases (&le I ). ThusThe effect cstimareswcrc
lacton for AMI.(listed in table 2). Quantitative defini- likely to be biased and therefore have not been presai-
tions of the diffaenr exposurr intensity catcpories were 4.
uscdfor organic solvents, benzene. and U F ."W. `modeme",and "high"exposure 10 organic solvenrscor- Statisisticalanalfies
responded to t--5%, 5-1546, and >15%, of the present When Only -& mMCMg ~CCOISsuch Bs @md gCn-
Swr?dishaccupational exposure limits;,reipmvely. For der are uscd, confounding can narmslly be rno* c,E-
knzene. rhc comspondingcargwics WEE 0.05-02,
ciently controlled in a suarified analysis rhan in a
0 2 4 . 5 , and ;.OS rngld. Exposure to ELMFwas c b - matched mnalyUu(45). In om smdy, all effat estimates
rified m x m i i i g u)S-hour arithmetic averages reported were therefore obtainedby uneandiritmllogis& rcgresl
for differem occuparions (441,with the fallowing cate- sion (36),sfzttified[or age into 3 b a d eaiipbrics (G4,
gories: 0.2%0.30.0.3043.50. and rO.50 pT. For #I 55-69,md 270 yean) md gender. Comprpison with
-. Mher occupational exposures. thedifferentexposurein- estimates from a conditional logistic regression model
tensity caregcnies ryere &heated by examplesofw u - (46)showed hah e stratification sufficiemlyaccounted
patioas or rasls. Pot txposurc to aromacic organic sol- for the cfftct of the matching vaiablcs. Year of diagno-
vents (exchdiq borneat), ChloridptedO I p i c solvents. L and county ofresidence did not influence the e f k t
and cytostatic drug. only dichoramous assessmznc (ex- cstimces and were therefore noT included. When rhe
posedhnexposed)was pdble. Expowretocattle7po~& [rends were tested,the m&icienr from a logistic mods1
rry mB fnesh mew was consideredtogether due to the hy- with h e exposureintensity (L=bobby-low, kmderate.
potherisofaannmon causal factor (animalhe v i m - 3=bigh)add dumian (as a continuous variabk). respec-
IS)-The main occuparion in this exposure catego- was tively, was IS^ as Ihr wt mrixic, ppovided drar tbtdata
fkllner.
were furly cmsisun! v,+krih such a model (47). Thzpop
Fm rtgular hair dye use and smoking. classificatiou ulrruon atrribucabh risk, with 95% cadfidence ialrarals
was dincrly bawdM the specificquestionsin he inrer- obtained witb tbc ManuA-Hacnszel qpmach, was esti-
view. Cases add refmatswere classified3s smokers if mated whcn appropriate (48,49).
rbeyhadmoLEdrwarlensr1 yearduringtheMyears
Tn wdcr to miucc cxponse midasdACadon, only
before &e dugnosisofthe case. Mure-time expornma expos^ assesswnts wilh bigh cbniideoctfaroccupa-
were asses& for9 tbe agmars,excepr EIUIIF.ionizing tional exposive~were used indK:a o a l y s ~ as l l b j a were
&ion and cb-puric
drugs.
classifiedas uncxpd fora particulara g a only if they
For &e occuparional expawms, rhc ~mfidzncein he were unexposed with bigk confidenceduring rbt tntirr:
mpmureoodinps was assessed (high CDafidonCc or not) &szssmeni period. subjects were clarified a i exposed
on the basis af the quality of informadm on worktasks 5&cy were e x p e d 4 t h bigb confidence for at bast 1
and erpoams in Ehe iareiviev data and the confidence y e w duing rhc assessmeni period. Subjects that could
of possibleexposure for differentworkrafks.
not bc classlftd as txpased Munexposedwith highcon-
kmte~rcbbiliy was assessed a f m the exposure frdcncc were excluded fromrheanalyses. A kss restric-
assessments were finabed for all the interview forms. tiveappwachdidMI change tbe results subsranrially. and
Tht main occupatiamlbygienisr (HW) reaq$essed198 they herefon have nor been presuftcd However, the
randomly sd~cltdirh\riew fomts. unawareof the arig- appmch implies that the psesented exposumdurations
inal exposure -KS.
h rbe ctrigiaal Lusessmenr47 and intentities are minimumvalues.
of these subjerns were dasSi3ed as ha- certainoccu-
pational OT Icim-t* exposue IO organic solvents,
70%of tbem were ctwrifid in same way in the itassesmen&The 193 iPerViews were alsor o s ~ ~ a bcyd Retvllr
aZndaecapMidhy~.Tbeconcardaawbetwcm
the 2 r c a p ~ e s s mw~as~s~iightly benn (8wL;shpn bc-
tweenrbenew and old assesuncnts;thisdifference indi-
caw Lt SIighS sbift ia asasmml with riw. However,
lb#wxenot&fkmws io &ecoac-bttween
he
wssaodrribartf. OntytbeoldassesrmentEw c n mcd
in the anai]nar of wpi%ufceffects.
Wecbwetoincludeinfmmrion on jwevjous chemo-
arm- h m beU~h e ir#crvicw d tht medical
d s (casesd y l in cbe chsihuian. sincetbe inter-
view was insensitive i m detecting such trcaunenls as
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T-415 P.06/11 F-465
-.
5 63 237 33
28
-25
10 65 288
7 a73 0.23-2.4
67 252 92 1.0 0.66-13
35 1196 0.56-1.7
28 1.1 6.8&+1
-IS
69 262
Ll82 0.35-1.9 0.98 0.64-15
indicatedan i-mg
risk with increasing intensity of
exposure [ m e 3, wsr fervend (hobby-low, maderape,
high),Pd).Ql]. Trpicrla t m p t.m s in rhc modcmc-high
intenshy caregory WCR painters and a b b e industry
workas. slrd in rbeIow-intensitycalcgory carpentersand
mtor mechanicsprevailed.
S u p d asvaciations were observed for eqosure
to kozene. bur not fcrr chlorinatedhyhnsbons. No in-
creasing Lislr by intensity of benzene txpowc WBS ob-
w e d . E f f e fFomexposum to organic sthcnts and
to benzene were separated by rzsmcrionof rhe analyses
rn mbjccrs c q w d 10 sokenrs othzr than benzene. The
odds ratio was 1.2 (95% CI 0.69-2.6) Tor the hobby-
low category and 27(%% CI 1.0-7.3) for them d x -
*high categoty;this m u I t indicates that the observed
cffcct was not due to be~llencexposwe aloae. Separa-
tion of the &acts from exposum IOall organic solvents
from rh3z of sromatic solvenu orher rhaa W n c was
not gossiblcbdeauhthey w e too closely associated.
Analyses by dunrion of only occupationalexposure
(ic,excluding kisure-rimzexposures) to all organic sol-
vents &Q indicated 2 positive assmiation with risk far
AML [1-7
0 2 case^, I5 rr4-u): OR 0.!38,45%
CT 0.44-2.2: 8-14 ye- (IS cases, 15 refmenu): OR
1.2. 95% CI -2.5;
215 y a ' ( 3 0 C- 17 nfet-
486 &and J Wwk Engiron NmNn 2#0, w26,cIa6
Albin er d
0355-3141
Apr-19-01 12:Zlpm FroM-
~ b mz t prevalmt qusure wag white spirit. For this
agenk thcokd-wouldconespolsd madcffccrlcv-
el of<lS rnghd, which is remarlrabiy LOW. In addition,
an effectfrom leisure-timc exposurr only [OR1.8,95%
cIO.92-33. WC in
WBS indirMed,
E- txposurc, which is Bn established risk as-
rnfar AML, did not fully explain &? e m s risk for ex-
pururc:to organic wlvents. +IkobservedleveIs of ben-
zene e x @ m were low(72% ofthe exposedcases were
e x p d to iarensities belnw 0.07 ppmj. uul our modest-
ly elevatedO R estimates fw benzene exposrule are thus
rlw ia conflictwith rRuseof formcr srudies.
We did not observean increased risk in association
with oven11c x p m topesticides.Thc fquent ust of
Uhxssion
prpxy mpdnJcals fw thecases didDOE p e d a classlfi-
catitioa of tbc type of peticicle. Our frnd-5 of no in-
?he salientfeature of the ~ 6 s e a ustudy was thz ccmsist- creaved risk with regard to the u ~ oef hair d y u am in
a t &ahan bemeenexp- m organic salvcslrs and acrordaaEewith rheresults of 2 f m m r studies {51,52),
1
risk for AML,c~pecidlyia cases wirh rrisamy a as rhe while 3 other mdjes[l9-21) have b mmo&stly sup
sole abwarion.Cmrrary to our hypochis, che a s s ~ c i a - portive of such a risk. Revibus studies of &e risk far
uoas were essentially Rondiffemwial with regard to the A M L associared c k h cxpogurc to ELMF are conflicting
O V pres~ence dclond ch.romosolllt!&mrmaliticr, as
well as co LOWur paltiidlosses ofchmrnosows5 and7, The hypothesis of an associarimh w e m suchexposure andtrLomy 8 was less sadng, having been Wed only
and indicate a modmrdy incmacdri* if any (26). C~IK
resulrs ate compatib[c with thistinding. We may, IO somr?extent.have underestimated the in-
Ensity and duration oexposure among the subjars by
oll a&w earlierpublicarioay (10,31,331. Inou1study, 7 out of 13 wirh 4 3 as a sole anomaly hada history of exposuretoorganic sdvmts (table4). a pnvakncesimilar to that rcporced by Dwico et a1 (33). It Is. in his contrxf. mtew0Ifby rbat a mriew of mament-nhtcd AML
ody wing m p s m jgsessmeftts with high confidwcc. Bias resmiting fronsuch miscldfication may be in eid m direction when mre than 2 exposmo categoriesare used in the analysis (53). However, for hoch fht cases
and referenu classified as expossd to organic sohrer~s.
did not reveal a s @ ~ t I y higherincidenceof uisomy 8 in such AML.w h camparedwirh de novoAML {7].
The possibility rbat expwure TO o r p i c solvents thus comulrsin difmntkaryotypic patterns thandoes exporn
to radio- or chcrnotkapy is fuitber suppond by rhe
the average number of years assessedwirh high c M -
dencewm I8 (out of20 possible); this fiading indicares that this is a minor problem. In addrim. we chose. rn the basis of pnviws&s of treaaneat-rehd AMlL
(13)and AMLrelatedtohighbenzew exposum(S),to
present lwk of an associaion bwbea exposure to solv c m and itbwmalitieS of ~ h r o ~ s a m5d asnd 7, aber-
rations that are commod id mstmc?nt-dated AML (7).
focus exposure assessmaton the 20 years before d q nosis. If kss inwnse, aad kss toxic, exposure is associacd wirh P longer lsrznCy t h e rhno 20 p&So,ur assess-
It remains to he sezn v t h e h other myeloid malignan- men&would u n k r r s ~ m w&vam cxpomwdurations
cies with trisomy 8 as a soh anomaly, especially myelo-
An i m p m r spcct of rhc vaIidiry af the study ist&e
dysphdc Syndtomcs and chronic myclopdiferaiivc dis- diffcrrndalUSE of proxy~ e q w d c mfsor cases amirefa-
orders [1). are also associated with exposure to organic enrs; rbis us(! violacesthe camparable accuwy principle.. .
solvents.
for;rhcselection ofrdcmns (55) and may lead TO negir-
The suggested higher risk for eryrhmhukmia rhaa rive damation bias. However, when there is no indica-
for other subtypes of AML in relation to exposunsto all rimb asubstantial difference ia in far ma ti^^qnality.the
organic solventsis inmesting,but it bas previously only dominsrlr usz:of pmxy ".pbAdentp for Lht:caacsand selfbeen repxd in relatian to a similar small number of r q x m EMxcfc=nts is justified (W.Thenfemts in our
cases frona pooled study (3I>and a case-seriesof kn- study rewned tht s ~ m icnediaanumher ofjobs held as
z e n e - e x w wcarbrr (91-
rht casts (table 1). In additian, no d&rcncc in the
Our dbsrrvations of censirtontty increased risb,.even n u m k of yzars assessedwih high mfidenct WSxecn
Awn low-kveicltposlsrr [not exceeding5% ofthe Swe+ ish accuparional cxpc~urclimits) to organic solvents are
a s o u t f e ofworry. The results also indicate rhat expo-
beween &C E B S ~ S&r&mntr f& expsuro ta OTgsolvents. Thus no substantialMerencz in infannation quality ws indicmd, b u ~tke ~ ~ S U X EaSre crude. W e
WIZ to osganic solvents m y concribwe IOan impomnr refrained fmm addingrrsponden~S f a N S US acovdate in ~ o p t i o dof &e A M L cases in&e generalpopulatiw. tht togietic r e p s i o n model becaosc such adjustments
488 scan6J Work ~nvimnHeal* MM. VOI2s. o 8
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F-46 5
1
do not secewidy nedpce tbe net bias (57). An effect e+ data entry. Asra Pcrsson and Gunnel Nilsson rzuicved
timate fororganic svIvencs lestricfad io self-ftspondenls the mcdical records.
did not indjcrte any subsranrialbias. SrilI, rhe dear dif-
The pmjm was sapponed by grants fromtbr Swcd-
ference in rhe pmpcmiun d ~ ~ ~ - d -i nk ~ivni c w ms ay ish C m c i l for Work Lift &search, rhe Swedish Can-
have Hecred the affect csricnares. Thjs possibility espe- cer Society, the Medical Fxulry of h a d Uoiverrity,
cially app1iesto cases diagnowd for DMrs people.
Lunds URivessity Hospital, Crunnar.Arvid and Elisakth
Although Iheassess men^ of exposure was made wirh- Nilsfoms Rt$earc.h Foundation, and PRBEM Resmch
out b l c d g o~f c a s c d m r st~m5h, r ethical m o n sI Founddon. The pmjcct w e a p p ~ v e dby the Ethics'
the nurseswho c m t d but tbc inmiews hadh i s bowl- Cbmmirlccof Lund University.
edge. This situcion may have inrroduced a ipositive)
bias, bot, in OUT opinion, it i s likely io have becd m a l l
since the interviews were nrherArmly svucNIzd
References
All refmals far cytogeneticinresrigsrionsare made
wilhin h e Swedish public bed&spun, and there is
dwcforc no reason to suspect any socioecmxnically
bared sekicm biasamong tbe cms, althoughcases di-
agnosed at older ages, whhl mrarive i d d therapy is
kss frequent,me likely u)be urrdtmprr+lented.A lower
pUr;cipar;oll RAILamong the mfuents rkan amoqs the cases may, however. h8VC introdtlceddifferentialseis-
daa into che uudy with rcgud ta,for example, socio-
ocmmmicfaam, aad &erefox resulred in biased e f f a
esfixwcs. Sucha seltction w d d be likely to invMJuce
a bias in the same directioa for bropd carzgaritsofex-
posure. We foundno iabicatimsof such a gencnl shift
inthtefFendmawsforindasajstl-utban(g~esnd
diesel fir4 and exhausr gases add ELf+=Golr s@cultUr-
f-m(pesticides, frefh-m~t-mimalcontact, fresh
wood) exposmw (table 2). bar u CBMOI btmlcd out-
The resulrs of a nasmafof expsrs\ae to organic
solvtms agreedwofl with rhcnsuhs aftbe initial il~ses5-
m e a Them wcre rn difftxeruxs in the rtpeement be-
cwen rhe c&sSandreferen&.
The medim durationof occupationatexposurewith-
in dose categaks was dightly higherforcases di-d
at olderages(261 yws),and the propdon of oexr-of-
kin inrerpiewswas higharhpdmIhe younge~age p u p ,
but it is ques~0a;lblewhether or nor thio differme LX-
plains the sugge!md effM mabrfica~mby age. Oned-
temarjveintaprera*wn Lrh;rrAhfLinddQccgohganic
solvcn~occprsa ~ a molder agefhim AML withothered-
o~.~possibiliyisan~g~cffectfros,slr-
p u r e in that it h a beEI snggatd thttse effect a f a
k-stagecarcimgm would b~ m4e prmpouacedat an
ddor age (58).
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