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Diss Factsheets
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EC number: 203-856-5 | CAS number: 111-30-8
- 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: Scientifically acceptable, well-documented study. Limitations in design/reporting but adequate for assessment.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 993
- Report date:
- 1993
Materials and methods
- Study type:
- cohort study (retrospective)
- Endpoint addressed:
- carcinogenicity
- Principles of method if other than guideline:
- A mortality analysis was performed in 186 men assigned to glutaraldehyde production from its start-up in 1959 through 1978, at a chemical plant in West Virginia and compared to US white males and 29000 chemical workers.
- GLP compliance:
- no
Test material
- Reference substance name:
- Glutaral
- EC Number:
- 203-856-5
- EC Name:
- Glutaral
- Cas Number:
- 111-30-8
- Molecular formula:
- C5H8O2
- IUPAC Name:
- glutaraldehyde
- Test material form:
- liquid
Constituent 1
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): Glutaraldehyde
Method
- Type of population:
- occupational
- Ethical approval:
- not applicable
- Details on study design:
- The cohort consisted of 186 men assigned to the glutaraldehyde production unit (GPU) from 1959 to 1978. These individuals were identified from work assignment information contained in the National Institute of Occupational Safety and Health/Union Carbide Corporation (UCC) mortality study of over 29,000 workers in the Kanawha Valley (KV) of West-Virginia. They were also a subset of UCC's ethylene oxide (EO) worker study, since these same operators were involved in the production of certain EO derivatives.
The vital status observation period was January 1, 1959 to December 31, 1983. Traditional Standardized Mortality Ratio (SMR) analyses, were conducted, using U.S. mortality rates for white males through 1988 for calculation of expected deaths. 10 Person years were calculated from first assignment to the GPU (after Dec. 31, 1958) to the date last observed. SMRs (observed/expected) were examined by time since first exposure and duration of assignment. In addition to external comparisons to the U.S. population, internal comparisons using the men from the KV cohort never assigned to the GPU as a referent group, were also conducted. - Exposure assessment:
- not specified
Results and discussion
- Results:
- Vital Status was ascertained for 181 (97.3%) study subjects and death certificates were available for all decedents. There were 14 deaths (7.5%) among the 186 study subjects. Race data were unavailable for 53 subjects. There were 125 known white and 8 known nonwhites in the study group. More than 50% of the cohort was first assigned to the GPU within the first five years of glutaraldehyde production and all subjects were observed at least 10 years with an average time since first exposure of 20.6 years. The average duration of assignment to the unit as of 1/1179 was 3.7 years.
There was a statistically significant deficit of deaths due to all causes with 14 observed and 25.4 expected (95% CI: 0.3, 0.9). The rate for total malignant neoplasms was also less than expected, with 4 cancer deaths versus 6.1 expected (SMR = 0.65). The cancer SMR was lower (0.52) for those who worked five years or more in the unit. The four cancers included one each due to stomach, lung and brain and a death due to lymphosarcoma, the only cancer death among those who worked more than 5 years in the production of glutaraldehyde. The number of cancer deaths expected among those assigned over 5 years was 1.9. The results of the internal comparisons of the glutaraldehyde workers to the remaining KV workers were consistent with those observed based on U.S. comparisons. There were no excess deaths due to all causes or total malignancies.
Applicant's summary and conclusion
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