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EC number: 200-831-0 | CAS number: 75-01-4
- 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:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: In the present record epidemiological data on developmental toxicity are combined. The studies have been published in peer-reviewed literature and are considered to be adequate for assessment.
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Carcinogenic, mutagenic, and teratogenic risks associated with vinyl chloride.
- Author:
- Infante, P.F., Wagoner, J.K. and Waxweiler, R.J.
- Year:
- 1 976
- Bibliographic source:
- Mutat Res 41:131-142
- Reference Type:
- publication
- Title:
- Congenital Central Nervous System Malformations and Vinyl Chloride Monomer Exposure: A Community Study.
- Author:
- Edmonds, L.D., Anderson, C.E., Flynt, J.W. and James, L.M.
- Year:
- 1 978
- Bibliographic source:
- Teratology 17:137-142.
- Reference Type:
- publication
- Title:
- Central nervous system malformations in relation to two polyvinyl chloride production facilities.
- Author:
- Rosenman, K.D., Rizzo, J.E., Conomos, M.G. and Halpin, G.J.
- Year:
- 1 989
- Bibliographic source:
- Archives Env Health 44:279-282.
- Reference Type:
- publication
- Title:
- Evaluation of the Association Between Birth Defects and Exposure to Ambient Vinyl Chloride
- Author:
- Theriault, G.; Iturra, H.; Gingras, S
- Year:
- 1 983
- Bibliographic source:
- Teratology 27, 359 - 370
Materials and methods
- Endpoint addressed:
- developmental toxicity / teratogenicity
- Principles of method if other than guideline:
- Epidemiological studies
- GLP compliance:
- no
Test material
- Reference substance name:
- Chloroethylene
- EC Number:
- 200-831-0
- EC Name:
- Chloroethylene
- Cas Number:
- 75-01-4
- Molecular formula:
- C2H3Cl
- IUPAC Name:
- chloroethene
Constituent 1
Method
- Type of population:
- general
Results and discussion
- Results:
- Although a statistically significant increase in congenital abnormalities has been observed in members of some communities near a vinyl chloride processing facility, reports have failed to establish a statistically significant association between developmental toxicity and either parental occupation or proximity to the facility.
Any other information on results incl. tables
Method
Analysis of numbers of congenital malformations in three communities in the northeast part of during 1970 - 1973. The three communities have PVC production plants.
Results
The rate of
malformations per 1,000 births for the three communities studied was
significantly higher than that in control areas (Table 1). The greatest
excess included malformations of the CNS, cleft lip and palate, club
foot and genital organs (Table 2).
Table 1
Malformation rates per 1000 live births in 3 selected
communities
Malformations
number number
Area Births Rate/1000 observed expected
Entire state 719,287 10.1 7295 --
of Ohio
Ashtabula 1,900 17.4 33* 19.3
Painesville 1,381 18.1 25* 14.0
Avon Lake 738 20.3 15* 7.5
Combined 4,019 18.2 73* 40.8
Table 2
Relative risk for specific congenical anomalies in three selected
communities including N Ridgeville
Number of defects
risk
Defects Observed expected ratio
All defects 109 56.0
1.95
Central nervous system 17 5.6 3.02
Cleft plate and lip 10 6.5
1.53
Genital organs 16 8.4
1.90
Clubfoot 23 8.2
2.79
all other defects 43 27.2
1.58
Reference
Infante et al. (1976)
Method
In a case control
study, analysis of incidence rates of central nervous system
malformations in infants born to residents of during 1970 - 1974 was
studied. (This county contains a PVC production plant).
Result
Incidence rates for
CNS malformations for residents are listed in Table 1. Although the
rates of central nervous system defects in infants born to residents of
were larger than in control areas, no relationship with parental
occupation or residential exposure was found. The parent’s place of
residence at time of infant's conception was determined and distances
from the PVC plant were measured for each case and control. There was
no significant difference between the two groups (p>0.4).
Table 1
CNS malformation rates for Kanawha County residents, 1970-1974
Defect Cases rate/10,000 births
anencephaly 23 14.1
Spina bifida 15 9.2
Hydrocephalus 7 4.3
Other CNS defects 2 1.2
Total CNS defects 47 28.8
Total white births 16,289
Reference
Edmonds et al. (1978).
Method
A case control study of all babies born with CNS effects in was conducted. The relationship of the cases and controls with two vinyl chloride plants were examined. For each subject, the distance from the subjects residence and each plant was determined.
Result
There was no relationship between proximity to the vinyl chloride plants and CNS or all birth defects combined.
Reference
Rosenman et al. (1989).
Method
Analysis of the
incidence of birth defects in infants born to residents of,during 1966
- 1979 with regard to relation to VC exposure was compared with three
other communities,, Baie-Comeau-Hauterive and. A case-control study was
also conducted.
Results
Although some data
from this study raised the hypothesis of an association between VC in
the air and birth defects in the exposed community, such an association
can not be substantiated within the sample size available (Table 1).
In the case-control phase of the study, the occupational and residential
histories of parents who gave birth to malformed infants were compared
with those of parents of normal infants. The two groups did not differ
in occupational exposure or closeness of residence to the VC
polymerization plant.
Birth-defect rates did not differ between school districts with high and
low VCM exposure, either for all birth defects or for CNS defects (Table
2). School districts adjacent to the plant did not differ from the
other school districts in numbers of birth defects (total or CNS), nor
did districts differ within and beyond a 1-mile radius of the plant.
Table 1
Number of malformed children observed in Shawinigan compared with three
comparison communities
expected
expected based on expected
based on Baie-Comeau based on
Parameter Shawinigan Drummondville Hauterive Rimouski
Total 159 102.68** 98.80**
124.08**
CNS 30 19.69*
18.18* 15.33**
Urogenital 30 19.15*
13.94** 13.14**
* p0.05; ** p0.01
Values only significant in all three comparison communities is presented.
Table 2
Birth defects between school districts with high and low VCM exposure
high exposure low exposure
total
births with defects 87
70 157
births without defects 2,285 2,125
4,410
births with CNS defects 16
13 29
births without CNS defects 2,356 2,182 4,538
Reference:
Theriault et al. (1983)
Applicant's summary and conclusion
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