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EC number: 200-663-8 | CAS number: 67-66-3
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Epidemiological data
Administrative data
- Endpoint:
- epidemiological data
- Type of information:
- other: cohort (retrospective) study in workers
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The study used sound methods with regard to the questionnaire building and the statistical evaluation of the questionnaire outcomes. However, the exposure information was taken into account only in a qualitative manner.
Data source
Reference
- Reference Type:
- publication
- Title:
- Pregnancy outcome of personnel in Swedish biomedical research laboratories
- Author:
- Wennborg H, Bodin L, Vainin H, Axelsson G
- Year:
- 2 000
- Bibliographic source:
- JOEM 42, 438-446
Materials and methods
- Study type:
- cohort study (retrospective)
- Endpoint addressed:
- toxicity to reproduction / fertility
Test guideline
- Qualifier:
- no guideline followed
- GLP compliance:
- no
Test material
- Reference substance name:
- Chloroform
- EC Number:
- 200-663-8
- EC Name:
- Chloroform
- Cas Number:
- 67-66-3
- Molecular formula:
- CHCl3
- IUPAC Name:
- trichloromethane
- Details on test material:
- Not applicable
Constituent 1
Method
- Type of population:
- occupational
- Ethical approval:
- not specified
- Details on study design:
- HYPOTHESIS TESTED (if cohort or case control study):
The rate of spontaneous abortions was higher for women who had ever worked in a laboratory compared to women who had never worked in a laboratory.
METHOD OF DATA COLLECTION
- Type: Questionnaire
- Details: A questionnaire was designed with one part probing the women's reproductive history and health status and another part with specific questions relevant to calculations of time to pregnancy during 1990 to 1994.
STUDY PERIOD:
January 1, 1990 through December 31, 1994
SETTING:
Sweden, women who had worked in universitary research laboratories or non-laboratory departments
STUDY POPULATION
- Total population (Total no. of persons in cohort from which the subjects were drawn): 1052
- Selection criteria: Women born in 1945 or later who had worked for 1 year or more during 1990 through 1994 in a biomedical research laboratory or non-laboratory department at Karolinska Institutet in Stockholm or at the universities of Gothenburg, Linköping, Lund, Stockholm, Umea, or Uppsala and had given birth to at least one child during that period.
- Total number of subjects participating in study: 763
- Sex/age/race: laboratory group: female/23 to 46 years/no data; non-laboratory group: female/23 to 50 years/no data
- Smoker/nonsmoker: no data
- Total number of subjects at end of study: 697
COMPARISON POPULATION
- Type: 1417 single births registered after 1973 in the Swedish Medical Register
OTHER DESCRIPTIVE INFORMATION ABOUT STUDY: - Exposure assessment:
- estimated
- Details on exposure:
- Exposure was estimated qualitatively on the basis of information about the women's education and profession. Each woman was asked about her work in any laboratory, the period during which it occurred, and the exposure to various agents including chemicals (organic solvents or other), radioactive isotopes, cell techniques, viruses, or bacteria during the months before conception. For solvents, specifically, the periods of use wwere requested with an accuracy margin of one month.
- Statistical methods:
- Statistical analyses. Analyses were performed with multiple logistic regression models for dichotomous outcomes: spontaneous abortions, SGA, LGA, high birth weight, preterm births, postterm births, and malformations. The effect parameter of the logistic model was an odds ratio. Birth weight as a continuous variable was analysed by multiple linear regression, the effect parameter being a regression coefficient with interpretation as a slope parameter, ie, the effect on the outcome of a unit increase in the explanatory variable.
In the initial analyses, the pregnancies were considered independent of one another. Subsequently, to take into account both possible constitutive biological factors specific for a given woman that might affect all of her pregnancies, as well as the cluster sampling scheme with the woman as the primary unit and her pregnancies as secondary units, refined analytical models were used. This accomplished primarily with mixed models in which a random effect for the woman-factor was introduced. We also used a simpler method to incorporated dependence into the logistic models for spontaneous abortions by adding a factor giving the number of previous miscarriages.
The analyses were performed with the Stata 6.0 software package. Specifically, we used the iis/xtlogit procedure in the analyses of random-effect models and iis/xtreg procedure for continuous outcomes.
Interaction factors were tested and goodness of fit was assessed in logistic models with the Hosmer-Lemeshow statistic. In the linear regression models, we used the R2 statistic and evaluation of log likelihood.
Results and discussion
- Results:
- For 622 women (856 pregnancies) who had worked during the period 1990 to 1994 the analyses of pregnancies for the women who had worked in laboratories relative to pregnancies for the women who had worked in non-laboratory departments yielded an unadjusted odds ratio for spontaneous abortion of 0.9 with a confidence interval 0.5 to 1.4. Table 1 shows the odds ratios obtained in analyses based on a model containing pregnancy-specific explanatory exposure variables for laboratory work, including certain solvents.
Any other information on results incl. tables
Table 1: Odds ratios obtained in analyses based on model containing pregnancy-specific explanatory exposure variables for laboratory work.
Exposure variable |
N |
Cases |
Odds ratio |
95 % confidence interval |
Cell techniques |
||||
NO |
676 |
56 |
1.0 |
-- |
YES |
180 |
17 |
1.3 |
0.6-2.5 |
Bacteria |
||||
NO |
695 |
56 |
1.0 |
-- |
YES |
161 |
17 |
1.2 |
0.5-2.9 |
Radioactive isotopes |
||||
NO |
566 |
48 |
1.0 |
-- |
YES |
290 |
25 |
0.8 |
0.4-1.6 |
Specific solvents |
||||
CHLOROFORM |
||||
NO |
770 |
60 |
1.0 |
-- |
YES |
86 |
13 |
2.3 |
0.9-5.9 |
Phenol |
||||
NO |
773 |
63 |
1.0 |
-- |
YES |
83 |
10 |
0.8 |
0.3-2.5 |
Use of other solvents |
||||
NO |
688 |
57 |
1.0 |
-- |
YES |
168 |
16 |
0.9 |
0.5-1.9 |
Applicant's summary and conclusion
- Conclusions:
- The study found a weak association between women working with chloroform in laboratories and spontaneous abortions.
- Executive summary:
An analysis of the effect of laboratory vs. non-laboratory work on the incidence of spontaneous abortions (lost of the embryo before gestational week 20) was performed on Swedish women born after 1945, who had worked for at least one year between 1990 and 1994 and given birth to at least one child during the period of 1990 to April 1995. To this end, a cohort of 1052 women was identified and questionnaires were sent to these women. The final analysis was performed on 622 women (856 pregnancies) who had responded to the questionnaire. The study found a slightly increased risk for spontaneous abortions among women working in laboratories with chloroform.
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