Document nx4b3DGV59agBD5ZmG9MDemw

Children's Health | Article Maternal Exposure to Occupational Solvents and Childhood Leukemia Claire Infante-Rivard,1 Jack Siemiatycki,2 Ramzan Lakhani,3 and Louise Nadon3 1Department of Epidemiology, Biostatistics, and Occupational Health, Faculty of Medicine, McGill University, Montral, Qubec, Canada; 2Dpartement de Mdecine sociale et prventive, Universit de Montral, Montral, Qubec, Canada; 3Institut National de la Recherche ScientifiqueInstitut Armand-Frappier, Laval, Qubec, Canada Many organic solvents are considered probable carcinogens. We carried out a population-based casecontrol study including 790 incident cases of childhood acute lymphoblastic leukemia and as many healthy controls, matched on age and sex. Maternal occupational exposure to solvents before and during pregnancy was estimated using the expert method, which involves chemists coding each individual's job for specific contaminants. Home exposure to solvents was also evaluated. The frequency of exposure to specific agents or mixtures was generally low. Results were generally similar for the period ranging from 2 years before pregnancy up to birth and for the pregnancy period alone. For the former period, the odds ratio (OR), adjusted for maternal age and sex, for any exposure to all solvents together was 1.11 [95% confidence interval (CI), 0.881.40]. Increased risks were observed for specific exposures, such as to 1,1,1-trichloroethane (OR = 7.55; 95% CI, 0.9261.97), toluene (OR = 1.88; 95% CI, 1.013.47), and mineral spirits (OR = 1.82; 95% CI, 1.053.14). There were stronger indications of moderately increased risks associated with exposure to alkanes (C5C17; OR = 1.78; 95% CI, 1.112.86) and mononuclear aromatic hydrocarbons (OR = 1.64; 95% CI, 1.122.41). Risk did not increase with increasing exposure, except for alkanes, where a significant trend (p = 0.04) was observed. Home exposure was not associated with increased risk. Using an elaborate exposure coding method, this study shows that maternal exposure to solvents in the workplace does not seem to play a major role in childhood leukemia. Key words: acute lymphoblastic leukemia, child, childhood leukemia, maternal occupational exposure, solvents. Environ Health Perspect 113:787792 (2005). doi:10.1289/ehp.7707 available via http://dx.doi.org/ [Online 3 March 2005] Acute lymphoblastic leukemia (ALL) is the most frequent form of cancer in children (National Cancer Institute of Canada 2004). At this time, there is only limited knowledge and evidence on environmental or other risk factors contributing to the incidence of ALL. Some convincing data show that ALL can arise in utero because characteristic chromosome translocations that generate chimeric fusion genes unique for each patient's leukemic clone are found at birth (Greaves 2002); therefore, the pregnancy and periconceptional periods are exposure windows of primary interest to study risk factors that could be involved in childhood ALL. Fetal exposure to chemical agents is likely to come primarily from maternal exposure at work. Among chemical agents with carcinogenic potential and to which a substantial proportion of workers are likely to be exposed are organic solvents. In a multisite casecontrol study of cancer patients in Montral, Canada, an estimated 40% of men had been occupationally exposed to at least one solvent over the course of their work careers (Siemiatycki 1991). A solvent is any substance capable of dissolving another substance to form a uniformly dispersed mixture or solution (Stacey 1993). In industrial processes, water, a polar solvent, is often incapable of dissolving a large number of substances, and therefore organic liquids are used. The expressions "industrial solvents" and "organic solvents" are conventionally applied to these organic liquids (Stacey 1993). Previous studies assessing parental occupational exposures for ALL have not always evaluated maternal exposures or have done so in studies of small size where a substantial proportion of mothers were homemakers, often leading to few usable results (Colt and Blair 1998). More recent and larger studies have included an assessment of maternal exposures; one reported "solvents" as an exposure category (Schuz et al. 2000), whereas another reported results on specific solvents or groups of solvents; but in both studies, exposure assignment seems to have been directly based on parents' self-reporting (Shu et al. 1999). Recently, McKinney at al. (2003) used parental self-report and a group of professionals to assign exposure to "occupational groups" (a mixture of occupations, industries, and groups of agents). Overall, results from previous studies that reported on solvents and leukemia have not been consistent. We conducted a casecontrol study of childhood leukemia using the expertise of trained chemists to determine maternal exposure to occupational solvents. Materials and Methods Case ascertainment. Details of the study have been described elsewhere (Infante-Rivard 2003; Infante-Rivard et al. 2000, 2001). Briefly, cases of ALL diagnosed between 1980 and 2000 in the province of Qubec, Canada, were recruited from tertiary care centers designated by governmental policy to hospitalize and treat children with cancer in the province. Tracing cases from these hospitals is equivalent to population-based ascertainment. Between 1980 and 1993 cases 09 years of age at diagnosis were recruited for study; between 1994 and 2000 case selection included those up to 14 years of age at diagnosis. A case was determined to have ALL (International Classification of Diseases, 9th Revision, code 204.0) (World Health Organization 1975) on the basis of a clinical diagnosis by an oncologist or a hematologist. Because cancer care is covered under a universal health plan, we believe that a negligible number of children, if any, were treated outside the province. Control selection. Population-based controls (one per case) were matched on sex and age at the time of diagnosis (calendar date) and thus were concurrently selected. From 1980 to 1993, the population-based controls were chosen from family allowance files (Rgie des Rentes du Qubec, Qubec, Canada). The family allowance is a government stipend awarded to all families with children living legally in Canada. This source of data was the most complete census of children for the study years. According to the expected distribution of cases based on matching criteria, a list of 10 potential controls was randomly chosen from the lists. Between 1994 and 2000, we used the provincial universal health insurance files (Rgie de l'Assurance Maladie du Qubec, Qubec, Canada) as a source for controls, which is an equivalently complete census of children. It was a better source of data for that time period because family allowances were more often directly deposited in the mother's bank account, which meant that the home address was no longer available in the file. We proceeded the same way to obtain potential controls. Address correspondence to C. Infante-Rivard, Department of Epidemiology, Biostatistics, and Occupational Health, Faculty of Medicine, McGill University, 1130 Pine Ave. West, Montral, Qubec, Canada H3A 1A3. Telephone: (514) 398-4231. Fax: (514) 398-7435. E-mail: claire.infante-rivard@ mcgill.ca The project was supported by grants from the National Health and Welfare Research and Development Program, Leukemia Research Fund of Canada, Canadian Institutes for Health Research, Fonds de la recherche en Sant du Qubec, and the Laboratory Center for Disease Control at Health Canada. The authors declare they have no competing financial interests. Received 29 October 2004; accepted 3 March 2005. Environmental Health Perspectives VOLUME 113 | NUMBER 6 | June 2005 787 Children's Health | Infante-Rivard et al. Study participants. Children who were adopted, who lived in foster families, whose families spoke neither French nor English, who did not reside in Canada, or whose parents were both unavailable for interview were excluded. We identified 848 eligible cases, and interviewed the parents of 790 (93.1%); of 916 eligible controls, 790 parents were interviewed (86.2%). The reasons for nonparticipation were confidential telephone number, refusal to participate, or inability to trace the family. The study was approved by each hospital's institutional review board as well as by the provincial agency regulating access to public databases with nominal information. We requested that the parents return a signed informed consent form for the interview. Data collection. Soon after the anticipated reception of a letter introducing participants to the general purpose of the study, trained interviewers contacted the parents to schedule an appointment for the interview, which was administered by telephone using structured questionnaires. Questionnaires were reviewed as they came in, and feedback was given regularly to interviewers. One questionnaire addressed general risk factors and potential confounders. To assess maternal occupational risk factors, the procedure was as follows: A complete job history was obtained from the mother for the period ranging from 18 years of age to the end of pregnancy. This information included the job title and dates on this job, and the type of industry and its name and address. For each job held by the mother from 2 years before pregnancy and up to birth of the index child, a semistructured questionnaire was used to probe the details of each job; as previously described (Goldberg et al. 2001), the information collected included the company's activities; raw materials used; machines used; goods produced; responsibilities for machine maintenance; type of room or building in which the woman worked; activities of workmates; presence of gases, fumes, dusts, biocides, oils, solvents, and ionizing and nonionizing radiation sources; use of area or personnel protective equipment; and a detailed open-ended description of the woman's typical activities at work. In addition, for frequent job titles and/or jobs with a significant potential for occupational exposures (e.g., nurse, sewing machine operator, hairdresser, waitress, cook, textile dry cleaner, knitting and weaving operator), a specialized questionnaire was also administered that Table 1. Matrix of specific chemicals, complex mixtures of chemicals, and chemical families used in the analysis. Chemical familiesb Codea 1 2 3456 7 Specific chemicals Methanol Ethanol Isopropanol Ethylene glycol Carbon tetrachloride Chloroform Methylene chloride 1,1,1-Trichloroethane Trichloroethylene Perchloroethylene Ethylene dichloride Acetone Methyl ethyl ketone Benzene Toluene Xylene Ethyl acetate Diethyl ether Turpentine Carbon disulfide Butyl cellosolve Mixtures Mineral spirits post-1970d Mineral spirits pre-1970d Leaded gasoline Unleaded gasoline Aviation gasoline Kerosene 232 XXc 233 XX 234 XX 235 XX 237 XX 238 XX 239 XX 240 XX 242 XX 243 XX 300 XX 248 XX 304 XX 252 XX 253 XX 254 XX 302 XX 250 280 266 306 202 Xe 203 X 191 X 299 X 190 X 195 X X X X X X X aThese codes were used by Siemiatycki (1991) to catalogue and define the various substances, and they can thus be used to easily find additional information on these chemicals in that reference. bChemical families: 1, alkanes (C5C17); 2, aliphatic alcohols; 3, chlorinated alkanes; 4, chlorinated alkenes; 5, aliphatic ketones; 6, mononuclear aromatic hydrocarbons; 7, aliphatic esters. cXX signifies that the agent listed to the left is a member of the chemical family indicated at the top. dBefore 1970, mineral spirits contained relatively higher amounts of benzene, toluene, and xylene due to ignorance of their toxic effects. eX signifies that the agent listed to the left contains components that are members of the chemical family indicated at the top. probed more deeply into the specific tasks, the time spent at them, specific exposures related to these tasks, and the environment in which they were conducted. Exposure coding. Exposure coding was carried out by a team of chemists and industrial hygienists who have many years of experience in exposure assessment in community-based casecontrol studies. They first assigned each occupation to standard Canadian industrial titles (at the three-digit level) and job titles (at the seven-digit level) (Statistics Canada 1980, 1992). The next step was to determine whether there was or was not exposure to specific solvents or chemical mixtures with solvents (listed in Table 1; discussed further below); the complete list of chemicals that were coded includes > 300 items, but the focus here is on solvents because these were the chemicals of primary interest of the study. The strategy to code exposures from individual job histories is termed the "expert method" in the occupational epidemiology literature (Teschke et al. 2002) and has been described previously (Grin et al. 1985; Siemiatycki et al. 1987). Briefly, experienced chemists use all the available information provided by the study subject, information accumulated from coding exposures for thousands of jobs held in the same geographical area (albeit for men) (Siemiatycki 1991), and their personal knowledge or consultants' knowledge of the industries. Chemists were blind to the case/control status. Each job held by the mother during the 2 years before pregnancy and during the pregnancy of the index child was coded separately. For each specific chemical or mixture of chemicals on our list, the chemists indicated the presence of exposure, their degree of confidence that the exposure had actually occurred ("possible," "probable," "definite"), the frequency of exposure during a normal work week (< 5, 530, or > 30% of the time, coded 1, 2, and 3, respectively), and the level of concentration. A low concentration (coded 1) was assigned if the subject had been exposed to a concentration slightly above background level in the general environment. A high concentration (coded 3) was assigned if the subject was exposed to the highest possible level of exposure for this chemical encountered in our study population--for example, if the subject was using a solvent herself in an enclosed area with poor ventilation. And a medium concentration (coded 2) was coded when the situation was intermediate. The list of agents coded (Table 1) includes several solvents. Some of these are specific chemicals (e.g., benzene, toluene), and some are complex mixtures of variable composition (e.g., mineral spirits, gasoline). A detailed definition of each specific agent listed in the table can be found elsewhere (Siemiatycki 1991). 788 VOLUME 113 | NUMBER 6 | June 2005 Environmental Health Perspectives Children's Health | Solvents and childhood leukemia Most are well-known agents whose meaning we have not altered from that conventionally understood. All the substances analyzed in this study can be used as industrial solvents, but they may have had other uses for the subjects studied here. For instance, benzene is a wellknown industrial solvent but can also be used as a chemical reagent; gasoline is more commonly known as fuel but can be used as a solvent, most notably by garage mechanics because it is readily available to them. Many of the agents fall into various chemical families, and many mixtures contain chemicals that fall into various chemical families. For seven chemical families (defined in Table 1), we regrouped subjects by means of the matrix in Table 1. In this matrix, the inclusion of a specific chemical signifies that it is part of the chemical family, and the inclusion of a mixture signifies that it includes chemicals that are part of that chemical family. Home exposure to solvents. The general questionnaire included items to assess exposure to solvents in the home: hobbies, such as model building, furniture stripping, and types of art work; activities carried out in and around the home with the potential for similar exposure, such as electronic and motor vehicle repair; and painting in the home. For each question, we asked who carried out the activity and during what time period, specified as 1 year before pregnancy, during pregnancy, and from birth to the reference date. Statistical analysis. Two time periods were defined: from 2 years before pregnancy up to birth, and during the specific pregnancy period. We used conditional logistic regression to estimate odds ratios (ORs) and 95% confidence intervals (CIs). Each agent, mixture, and family was analyzed in a separate model, and the analyses were adjusted for maternal age and level of schooling. Results are first presented contrasting any exposure with no exposure. For the exposure period ranging from 2 years before pregnancy up to birth, we repeated the analysis contrasting "any exposure" with "no exposure" but this time taking into account the chemist's confidence factor in coding. In the latter analysis, if the chemist had coded the exposure as "possible" (vs. "probable" and "definite"), exposure was assigned to the "no exposure" category. For the same time window, we also conducted an analysis with three levels of exposure: level 0 (baseline), no exposure (defined as none coded or exposure coded with a "possible" confidence); level 1, some exposure (exposure resulting in concentration frequency < 4), and level 2, greater exposure (concentration frequency 4). Finally, we used a model that includes all specific agents and mixtures. We analyzed residential exposure to solvents in the household as never/ever for each question. Results The distribution of sociodemographic characteristics between cases and controls was quite similar (Table 2). More than 99% of mothers in both the case and control groups answered their own questionnaires. The proportion of women with gainful employment in both groups was almost equal (Table 3). Control mothers had an average of 1.33 jobs over the study period, whereas case mothers had an average of 1.29 jobs. Thirteen job titles among the 15 most frequently held jobs were similar between case and control mothers. There were more sewing machine operators and cosmetologists among case mothers than among control mothers. Most exposure frequencies to specific agents or mixtures in the period spanning from 2 years before pregnancy to birth were low (data not shown). For individual chemicals and mixtures, case mothers were more often exposed than were control mothers to 1,1,1-trichloroethane (7 vs. 1), toluene (32 vs. 19), turpentine (5 vs. 3), methyl ethyl ketone (4 vs. 0), mineral spirits (45 vs. 21), and leaded gasoline (5 vs. 3). However, control mothers were more often exposed to methanol (30 vs. 20), isopropanol (134 vs. 121), chloroform (10 vs. 2), diethyl ether (12 vs. 7), benzene (8 vs. 4), and unleaded gasoline (8 vs. 6). With respect to chemicals regrouped under chemical families, except for aliphatic alcohols (cases = 168; controls = 191), cases were more often found to be exposed than controls (alkanes, 56 vs. 32; aliphatic ketones, 23 vs. 19; mononuclear aromatic hydrocarbons, 95 vs. 63), or the frequency was the same (chlorinated alkanes, 22 vs. 21; chlorinated alkenes, 12 vs. 12). Exposure to the general category of solvents (331 vs. 322) was similar in both groups. In Table 4, we show adjusted ORs for exposure to specific chemicals, mixtures, chemical families, and the general "solvents" category. Differences in the ORs between the two periods (2 years before pregnancy and up to birth and only during pregnancy) were minor. The same number of women were working in both periods, but a smaller number of jobs were held during the pregnancy period, reducing the opportunities for exposure. With respect to the individual agents and the mixtures, increased risks were observed for 1,1,1trichloroethane, toluene, mineral spirits, and leaded gasoline. There were stronger indications of moderately increased risks associated with alkanes (C5C17) and mononuclear aromatic hydrocarbons for both periods. No risk increase was observed for the general category of solvents. Table 2. Demographic characteristics [no. (%)] of ALL cases and controls. Cases Mother's education None or primary school Secondary school College or university Mother's age at child's birth < 35 35 Family income at diagnosis (Can$) 40,000 10,00039,000 < 10,000 Cases (n = 790) 34 (4.3) 437 (55.3) 319 (40.4) 721 (91.3) 69 (8.7) 312 (39.9) 427 (54.7) 42 (5.4) Population controls (n = 790) 25 (3.2) 436 (55.2) 328 (41.6) 743 (94.0) 47 (6.0) 309 (40.2) 422 (54.9) 38 (4.9) Table 3. Distribution of job titles among mothers of ALL cases and population controls during the period ranging from 2 years before pregnancy up to birth of the index child. Cases Controls No. not working (%) No. working No. of jobs held (average per person) Job titles by order of frequency (highest to lowest) 178 (22.5) 612 792 (1.29) Secretary Clerk (general office) Sewing machine operator Waitress Cashier (clerical) Nurse (general duty) Cosmetologist Sales clerk Teller Elementary school teacher Baby sitter Receptionist Computer operator Accountant clerk Nurse's aide 173 (21.9) 617 820 (1.33) Secretary Clerk (general office) Waitress Nurse (general duty) Cashier (clerical) Teller Sales clerk Elementary school teacher Sewing machine operator Cashier (customer service) Cosmetologist Receptionist Baby sitter Accountant clerk Counterwoman (cafeteria) Environmental Health Perspectives VOLUME 113 | NUMBER 6 | June 2005 789 Children's Health | Infante-Rivard et al. Results comparing exposed with nonexposed mothers accounting for confidence in the coding are shown in Table 5; ORs are quite similar to those reported in Table 4, where confidence level was not considered, except possibly for methylene chloride and chlorinated alkanes, where they are higher. Exposure frequencies at the highest level were very low (< 1% for most contaminants), and there was no indication of increased risk with Table 4. Adjusteda OR (95% CI) and ratio of discordant pairs (RDP) for maternal exposure to solvents. 2 years before pregnancy up to birth ORb (95% CI) RDP During pregnancy OR (95% CI) RDP Specific chemicals Methanol Ethanol Isopropanol Chloroform Methylene chloride 1,1,1-Trichloroethane Perchloroethylene Acetone Methyl ethyl ketone Benzene Toluene Diethyl ether Turpentine Mixtures Mineral spirits, post-1970 Minerals spirits, pre-1970 Leaded gasoline Unleaded gasoline Chemical familiesc Alkanes (C5C17) Aliphatic alcohols Chlorinated alkanes Chlorinated alkenes Aliphatic ketones MAH Solventsd 0.77 (0.411.47) 1.22 (0.662.25) 0.96 (0.711.29) 0.25 (0.051.17) 1.34 (0.543.34) 7.55 (0.9261.97) 0.96 (0.412.25) 1.05 (0.532.08) -- 0.82 (0.223.06) 1.88 (1.013.47) 0.50 (0.171.48) 1.76 (0.427.42) 1.82 (1.053.14) -- 5.09 (0.5943.65) 0.90 (0.302.71) 1.78 (1.112.86) 0.90 (0.681.18) 1.33 (0.682.61) 0.97 (0.432.17) 1.30 (0.682.50) 1.64 (1.122.41) 1.09 (0.871.38) 17:22 23:19 85:89 2:8 11:8 7:1 11:11 17:16 4:0 4:5 29:16 5:15 5:3 37:20 5:0 5:1 6:7 48:27 97:108 20:15 12:12 21:16 70:43 154:141 0.78 (0.391.55) 1.06 (0.552.03) 0.95 (0.691.31) 0.25 (0.051.17) 1.25 (0.463.35) 4.07 (0.4536.7) 0.84 (0.302.34) 1.13 (0.522.44) -- 1.39 (0.316.25) 2.25 (1.024.95) 0.63 (0.201.93) 1.76 (0.427.42) 1.66 (0.863.22) -- 4.14 (0.4637.16) 0.83 (0.223.10) 1.72 (0.983.03) 0.89 (0.661.20) 1.05 (0.502.19) 0.86 (0.332.25) 1.46 (0.703.03) 1.68 (1.062.67) 1.00 (0.781.28) 15:19 19:18 73:78 2:8 9:7 4:1 7:8 14:12 4:0 4:3 20:9 5:8 5:3 24:14 4:0 4:1 4:5 33:19 84:95 15:14 8:9 18:12 49:29 125:125 MAH, mononuclear aromatic hydrocarbons. aAdjusted for maternal age and level of schooling; specific chemicals or mixtures with fewer than four exposed mothers are not shown. bOdds ratio (95% CI) for any exposure; baseline is no exposure. cChemical families regroup specific chemicals that belong to a family and mixtures that have components belonging to it. dIncludes all specific chemicals and mixtures in the table. Table 5. Adjusted ORsa (95% CIs), versus possible/no exposure, for levels of maternal exposure to solvents during the 2 years before pregnancy up to birth. Probable/definite Level 1b Level 2c Specific chemicals Methanol Ethanol Isopropanol Chloroform Methylene chloride Perchloroethylene Acetone Benzene Toluene Diethyl ether Turpentine Mixtures Mineral spirits, post-1970 Chemical familiesd Alkanes (C5C17)* Aliphatic alcohols Chlorinated alkanes Chlorinated alkenes Aliphatic ketones MAH Solventse 0.81 (0.431.55) 1.11 (0.592.08) 0.97 (0.721.31) 0.16 (0.021.36) 3.22 (0.8811.73) 0.87 (0.352.18) 1.11 (0.542.29) 0.77 (0.173.48) 1.98 (1.063.72) 0.63 (0.201.94) 1.76 (0.427.42) 1.74 (0.993.06) 1.78 (1.092.91) 0.91 (0.691.20) 2.00 (0.904.47) 0.89 (0.372.11) 1.40 (0.712.77) 1.67 (1.132.48) 1.11 (0.881.40) 0.81 (0.381.70) 1.44 (0.613.39) 0.92 (0.651.32) 0.30 (0.032.90) 4.68 (0.5540.20) 0.95 (0.352.55) 0.95 (0.392.28) -- 3.19 (1.437.12) 0.67 (0.192.41) 1.64 (0.279.92) 1.60 (0.862.98) 1.56 (0.912.67) 0.89 (0.641.23) 2.18 (0.677.10) 1.07 (0.412.80) 1.24 (0.542.84) 1.82 (1.152.87) 1.11 (0.851.46) 0.82 (0.252.77) 0.81 (0.322.07) 1.09 (0.651.84) -- 2.49 (0.4812.81) 0.55 (0.056.34) 1.55 (0.435.51) 1.47 (0.258.85) 0.68 (0.1822.05) 0.51 (0.045.59) 2.00 (0.1822.05) 2.50 (0.669.46) 3.39 (0.9412.21) 0.95 (0.601.51) 1.86 (0.625.57) 0.35 (0.033.53) 1.80 (0.526.17) 1.32 (0.622.80) 1.11 (0.751.63) MAH, mononuclear aromatic hydrocarbons. aAdjusted for maternal age and level of schooling. bDefined as concentration frequency < 4; baseline is possible or no exposure. cDefined as concentration frequency 4. dChemical families regroup specific chemicals that belong to a family and mixtures that have components belonging to it. eIncludes all specific chemicals and mixtures in the table. *p-Value for trend = 0.04. increased level of exposure, except for alkanes, where a significant trend (p = 0.04) was observed. Another analysis was carried out including in the model all the specific chemicals and mixtures, except those with empty cells, and using the entire target period. Those results show that 1,1,1-trichloroethane (OR = 8.16; 95% CI, 0.8578.35), toluene (OR = 1.94; 95% CI, 0.983.84), leaded gasoline (OR = 8.16; 95% CI, 0.8578.35), and mineral spirits (OR = 1.76; 95% CI, 0.973.19) remained associated with increased risks. Finally, with respect to residential exposure to solvents, we found no increased risk associated with any activity, including those involving the postnatal period (data not shown). Discussion The distributions of jobs between case and control mothers were remarkably similar, with a few exceptions, the main one being that there were more sewing machine operators in the case group. This was previously reported for the study subjects included between 1980 and 1993 (Infante-Rivard and Deadman 2003). Despite the fact that prevalence of any exposure to unspecific solvents as a whole was substantial, that to specific agents or mixtures was low and even lower at the highest levels for these agents. For the "solvents" category, cases and controls had a similar exposure prevalences. Among the specific agents and mixtures to which mothers were exposed before or during pregnancy and that were associated with increased risk of ALL were 1,1,1-trichloroethane, toluene, mineral spirits, leaded gasoline, and possibly methylene chloride and methyl ethyl ketone. Among the chemical families, there were stronger indications of increased risk for alkanes (C5C17) and mononuclear aromatic hydrocarbons. In a recent review on organic solvents and cancer, Lynge et al. (1997) reported that there is some evidence for an increased risk of cancer with toluene, 1,1,1-trichloroethane, and methylene chloride, although none is classified yet as a carcinogen by any regulatory agency. The U.S. National Institute for Occupational Safety and Health (NIOSH 1978) issued a bulletin on chloroethanes stating that 1,1,1trichloroethane should be treated in the workplace with caution because of its structural similarity to other chloroethanes shown to be carcinogenic in animals. Mineral spirits are refined petroleum solvents that include varnish makers' and painters' naphtha, Stoddard solvent, and white spirits (Siemiatycki 1991). They are largely composed of saturated hydrocarbons (or alkanes, which in liquid form are C5C17), but also include a small proportion of benzene. Although benzene is a recognized leukemogenic agent [International Agency for Research on Cancer (IARC) 1987], there is 790 VOLUME 113 | NUMBER 6 | June 2005 Environmental Health Perspectives Children's Health | Solvents and childhood leukemia little information on the carcinogenicity of mineral spirits as such; a Swedish study reported an increased risk of acute leukemia among painters (Lindquist et al. 1987), but painters may be exposed to a greater extent to other solvents such as toluene and xylene. Leaded gasoline, another mixture that showed indications of increasing risk, is a mixture of hydrocarbons used as fuel for automobiles; it also contains benzene and toluene. A fairly consistent link between fathers with occupations in motor-vehiclerelated occupations and childhood leukemia has been reported (Colt and Blair 1998); however, such occupations involve exposure to a variety of chemicals, including polycyclic aromatic hydrocarbons such as benzo[a]pyrene, which is considered a probable or suspected carcinogenic agent by regulating agencies (IARC 1983). Results from studies on maternal occupational exposures and childhood ALL published between 1980 and 1997 (Feingold et al. 1992; Gold et al. 1982; Hemminki et al. 1981; Lowengart et al. 1987; Magnani et al. 1990; McKinney et al. 1987; Olsen et al. 1991; Shu et al. 1988; Van Steensel-Moll et al. 1985) have been reviewed before (Colt and Blair 1998). In all these studies except that by Feingold et al. (1992), exposure was defined as having an occupation or belonging to an exposed industry, or occasionally, exposure to a specific agent was reported, as determined by maternal reporting. This strategy was also used in a more recent study from Germany (Schuz et al. 2000) not included in the review. On the other hand, Feingold et al. (1992) used a general job-exposure matrix to determine exposure to a list of specific agents; unfortunately, this study was very small (~ 60 cases of ALL and 60 controls), and results were inconclusive. In a more recent and large study from the United States (Shu et al. 1999), mothers reported specific exposures as well as the approximate length of time spent being exposed to a particular agent. No additional strategy to code exposure involving chemists or similar experts is explicitly described, so it is assumed that the self-reported exposures were used as such. Finally, in another recently published and large study, this time from the United Kingdom (McKinney et al. 2003), occupations and industries were coded according to standard classifications; in addition, a panel of experts, including a hygienist, created 31 occupational groups that were said to be homogeneous for specific exposures. The occupational groups used in the analysis include job titles (e.g., leather workers), sectors of activity (e.g., agriculture), and agents such as solvents and hydrocarbons (skin/epidermal or inhaled particulate). The method to create the groups is not detailed in the report. Because of the different ways to classify exposures and the multiple classifications used (even for job titles or industries, each study using their respective national classification), results are difficult to compare. However, in the three more recent studies (McKinney et al. 2003; Schuz et al. 2000; Shu et al. 1999), an explicit "solvents" category was used, and results are as follows: Schuz et al. (2000) report an OR of 1.2 (95% CI , 0.91.7) for exposure to solvents during periconception and a similar result during pregnancy. Shu et al. (1999) report an OR of 1.8 (95% CI, 1.32.5) for exposure to "possible organic solvents" during preconception (2 years before conception) and a similar result during pregnancy. McKinney et al. (2003) report an OR associated with exposure to solvents at periconception of 1.0 (95% CI, 0.661.51); however, exposure to "dermal hydrocarbons" had an OR of 2.16 (95% CI, 1.164.02). The present study uses the most detailed and elaborate exposure assessment method in comparison with previous studies. The expert method used here has been found to have good validity (Fritschi et al. 2003). Its steps have been clearly detailed (Siemiatycki 1991), and results using this method to uncover carcinogens in community-based casecontrol studies have been abundantly published (Aronson et al. 1996; Parent et al. 2000). In this study, all specific agents associated with increased risk have also been associated with increased risks of cancer in previous studies. Although results for some specific agents or families indicated increased risk, this was not as clear for the general category "solvents." The families of alkanes (C5C17) and mononuclear aromatic hydrocarbons are ones that many previous studies have tried to capture by using the hydrocarbon-related occupations (Lowengart et al. 1987; McKinney et al. 2003; Olsen et al. 1991; Shu et al. 1988, 1999; Van Steensel-Moll et al. 1985). The result by McKinney et al. (2003) showing a substantial increase in risk associated with periconception dermal exposure to hydrocarbons is consistent with our own. Overall, our results on alkanes and mononuclear aromatic hydrocarbons are consistent with and reinforce previous results. However, except for alkanes, it was disconcerting to find no indication of an exposureresponse relationship, an observation also reported by Shu et al. (1999). A study reported results on home exposure to solvents and childhood ALL (Freedman et al. 2001). Only artwork at a frequency of more than four times a month was associated with an increased risk of ALL. We did not measure frequency of exposure for home solvents, but none of the ORs in our study indicated any increase in risk for the ever-exposed category. In comparison with previous studies on parental occupational exposures and childhood ALL, this is the third largest study in terms of number of cases. Nevertheless, power is still an issue. With respect to potential biases often affecting casecontrol studies, in this study selection bias was unlikely: participation rates for cases and especially for controls were markedly higher (by ~ 20%) than in any of the other large studies cited. However, although the exposure assignment method used in this study seems more refined than in previous studies, it is safe to say that nondifferential misclassification of exposures affected the results and reduced our ability to uncover significant findings. In conclusion, this study used an exposure assignment method that is among the best available for community-based casecontrol studies of cancer. The results gave more specific indications than previous studies and point to an increase in ALL risk associated with maternal exposure to occupational alkanes and mononuclear aromatic hydrocarbons. Nevertheless, the results are still somewhat uncertain. From a public health point of view, it was reassuring to observe that, as in all previous studies, maternal exposures were most often rare and occurred at low levels; this, of course, makes the task of uncovering effects more difficult. However, this fact should not deter us from a continued search in this direction because prenatal exposure to carcinogens as risk factors for childhood leukemia makes biologic sense, and even low levels during this period could be damaging. We are thus challenged to develop more sensitive methods to ascertain parental occupational exposures. Adding a genetic susceptibility perspective could also enhance our ability to uncover the susceptible dyads (mother and child). REFERENCES Aronson KJ, Siemiatycki J, Dewar R, Gerin M. 1996. Occupational risk factors for prostate cancer--results from a case-control study in Montreal, Quebec, Canada. Am J Epidemiol 143:363373. Colt JS, Blair A. 1998. Parental occupational exposures and risk of childhood cancer. Environ Health Perspect 106(suppl 3):909925. Feingold L, Savitz DA, John EM. 1992. Use of a job-exposure matrix to evaluate parental occupation and childhood cancer. Cancer Causes Control 3:161169. Freedman DM, Stewart P, Kleinerman RA, Wacholder S, Hatch EE, Tarone RE, et al. 2001. Household solvent exposures and childhood acute lymphoblatic leukemia. Am J Public Health 91:564567. Fritschi L, Nadon L, Benke G, Lakhani R, Latreille B, Parent ME, et al. 2003. Validation of expert assessment of occupational histories. Am J Ind Med 43:519522. Grin M, Siemiatycki J, Kemper H. 1985. Obtaining occupational exposure histories in epidemiological case-control studies. J Occup Med 27:420427. Gold EB, Diener MD, Szklo M. 1982. Parental occupations and cancer in children. J Occup Med 24:578584. Goldberg MS, Parent ME, Siemiatycki J, Dsy M, Nadon L, Richardson L, et al. 2001. A case-control study of the relationship between the risk of colon cancer in men and exposures to occupational agents. Am J Ind Med 39:531546. Greaves M. 2002. Childhood leukaemia. Br Med J 324:283287. Hemminki K, Saloniemi I, Salonen T, Partanen T, Vaino H. 1981. Chlidhood cancer and parental occupation in Finland. J Epidemiol Commun Health 35:1115. Environmental Health Perspectives VOLUME 113 | NUMBER 6 | June 2005 791 Children's Health | Infante-Rivard et al. IARC. 1983. Overall evaluations of carcinogenicity. Polynuclear Aromatic Compounds, Part 1: Chemical, Environmental and Experimental Data. IARC Mon Eval Carcinog Risks Hum 32:1477. IARC. 1987. Overall evaluations of carcinogenicity: an updating of IARC Monographs Volumes 1 to 42. IARC Monogr Eval Carcinog Risks Hum suppl 7:1440. Infante-Rivard C. 2003. Hospital or population controls for cases of severe childhood diseases? Am J Epidemiol 157:176182. Infante-Rivard C, Deadman JE. 2003. Maternal occupational exposure to extremely low magnetic fields during pregnancy and childhood leukemia. Epidemiology 14:437441. Infante-Rivard C, Fortier I, Olson E. 2000. Markers of infection, breast-feeding and childhood acute lymphoblastic leukemia. Br J Cancer 83:15551564. Infante-Rivard C, Olson E, Jacques L, Ayotte P. 2001. Drinking water contaminants and childhood leukemia. Epidemiology 12:1319. Lindquist R, Nilsson B, Eklund G, Gahrton G. 1987. Increased risk of developing acute leukemia after employment as a painter. Cancer 60:13781384. Lowengart RA, Peters JM, Cicioni C, Buckley J, Bernstein L, Preston-Martin S, et al. 1987. Childhood leukemia and parents' occupational and home exposures. J Natl Cancer Inst 79:3946. Lynge E, Anttila A, Hemminki K. 1997. Organic solvents and cancer. Cancer Causes Control 8:406419. Magnani C, Pastore G, Luzzatto L, Terracini B. 1990. Parental occupation and other environmental factors in the etiology of leukemias and non-Hodgkin's lymphoma in childhood; a case-control study. Tumori 76:413419. McKinney PA, Cartwright RA, Saiu JMT, Mann JR, Stiller CA, Draper GJ, et al. 1987. The inter-regional epidemiological study of childhood cancer (IRESCC): a case control study of aetiological factors in leukaemia and lymphoma. Arch Dis Child 62:279287. McKinney PA, Fear NT, Stockton D, on behalf of the UK Childhood Cancer Study Investigators. 2003. Parental occupation at periconception: findings from the United Kingdom Childhood Cancer Study. Occup Environ Med 60:901909. National Cancer Institute of Canada. 2004. Canadian Cancer Statistics 2004. Toronto:National Cancer Institute of Canada. Available: http://www.cancer.ca [accessed 20 October 2004]. NIOSH. 1978. Current Intelligence Bulletin 27. Chloroethanes: Review of Toxicity. 21 August. Cincinnati, OH:National Institute for Occupational Safety and Health. Olsen JH, de Nully Brown P, Schulgen G, Schulgen G, Moller Jensen O. 1991. Parental employment at time of conception and risk of cancer in offspring. Eur J Cancer 27:958965. Parent ME, Hua Y, Siemiatycki J. 2000. Occupational risk factors for renal cell carcinoma in Montreal. Am J Ind Med 38:609618. Schuz J, Kaletsch U, Meinert R, Kaatsch P, Michaelis J. 2000. Risk of childhood leukemia and parental self-reported occupational exposure to chemicals, dusts, and fumes: results from pooled analyses of German population-based case-control studies. Cancer Epidemiol Biomarkers Prev 9:835838. Shu XO, Gao YT, Brinton LA, Linet MS, Tu JT, Zheng W, et al. 1988. A population-based case-control study of childhood leukemia in Shanghai. Cancer 62:635644. Shu XO, Stewart P, Wen WQ, Potter JD, Buckley JD, Heineman E, et al. 1999. Parental occupational exposure to hydrocarbons and risk of acute lymphocytic leukemia in offspring. Cancer Epidemiol Biomarkers Prev 8:783791. Siemiatycki J. 1991. Risk Factors for Cancer in the Workplace. Boca Raton, FL:CRC Press. Siemiatycki J, Wacholder S, Richardson L, Dewar R, Grin M. 1987. Discovering carcinogens in the occupational environment. Scand J Work Occup Environ Health 13:486492. Stacey NH. 1993. Toxicity of solvents. In: Occupational Toxicology (Stacey NH, ed). London:Taylor & Francis, 205212. Statistics Canada. 1980. Standard Industrial Classification. Publication 12-501/1980Eed. Ottawa, Ontario:Statistics Canada. Statistics Canada. 1992. Standard Occupational Classification. Publication MP53-25/1992Eed. Ottawa, Ontario:Statistics Canada. Teschke K, Olshan AF, Daniels JL, De Roos AJ, Parks CG, Schultz M, et al. 2002. Occupational exposure assessment in case-control studies: opportunities for improvement. Occup Environ Med 59:575594. Van Steensel-Moll HA, Valkenburg HA, Van Zanen GE. 1985. Childhood leukemia and parental occupation. Am J Epidemiol 121:216224. World Health Organization. 1975. International Classification of Diseases, 9th Revision. Geneva:World Health Organization. 792 VOLUME 113 | NUMBER 6 | June 2005 Environmental Health Perspectives