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EC number: 202-710-8 | CAS number: 98-88-4
- 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:
- other information
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- The study is inconclusive on the specific impact of benzoyl chloride on workers since the chemical plant investigated produces many chlorinated compounds. Besides, some bias in the study design are reported. However, the study is generally well described and conducted with accepted scientific principles. This study should therefore be considered as valid with restrictions.
Data source
Materials and methods
- Study type:
- cohort study (retrospective)
- Endpoint addressed:
- carcinogenicity
- Principles of method if other than guideline:
- Mortality rates were investigated among British workers exposed to benzotrichloride (98077), benzal-chloride (98873), benzyl-chloride, (100447), and benzoyl-chloride (98884) at a factory that manufactured chlorinated toluenes. The study population included 163 exposed and 790 unexposed factory workers employed for at least 6 months between 1961 and 1970. Death certificates were reviewed for the 91 subjects known to have died. Standardized Mortality Ratios (SMRs) were calculated using the mortality rates of the general population of England and Wales as comparison. A second analysis was performed using the Regression Models in Life Tables technique.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Benzoyl chloride
- EC Number:
- 202-710-8
- EC Name:
- Benzoyl chloride
- Cas Number:
- 98-88-4
- Molecular formula:
- C7H5ClO
- IUPAC Name:
- benzoyl chloride
- Details on test material:
- No data
Constituent 1
Method
- Details on study design:
- HYPOTHESIS TESTED (if cohort or case control study):
- In the standardized mortality ratio approach: The mortality of the study population after adjustments for age and calendar year is similar to the rates of mortality for England and Wales as a whole.
- in the regression models in life-tables approach: null hypothesis is a no effect from exposed people upon cause-specific mortality.
METHOD OF DATA COLLECTION
- Type: Record review was provided by the company investigated presenting contact details of former employees. Mortality rates for the investigated population was checked at the office of population, censures and surveys
No further details
STUDY PERIOD: Between 1961 and 1976 (included).
SETTING:
STUDY POPULATION
- Total population (Total no. of persons in cohort from which the subjects were drawn): 953
- Selection criteria: people working in the chemical plant for at least 6 months at the beginning of the study
- Sex/age/race: male workers aged at least 24
No further data
COMPARISON POPULATION
- Type: Control or reference group assessed to be not exposed to chlorinated compounds
No further data
HEALTH EFFECTS STUDIED
- Disease(s): cancers
- Other health effects: mortality
No further data - Exposure assessment:
- estimated
Results and discussion
- Results:
- STATISTICAL RESULTS
- SMR (Standard mortality ratio): For all causes and for causes other than cancer, SMRs tended to increase with time since first employment. Elevated SMRs were found among the exposed group for all causes, all cancers, digestive system cancers, and respiratory system cancers. The unexposed group had elevated SMRs for cancers of the buccal cavity and throat. For both groups of workers combined, SMRs were increased for all causes and all cancers
- Other:
Using the Life Tables, cancer mortality was increased only in exposed workers who had first been employed before 1951.
No further data - Confounding factors:
- Exposure and observation periods overlap may be subject to artefacts such as the 'survivor population effect'. Smoking status of some people included in the experiment was not known.
- Strengths and weaknesses:
- Categorization of the whole population included in this experiment was done in two times, it may have introduce a bias. Besides, the size of investigated cohorts is a bit small for statistical significance.
Applicant's summary and conclusion
- Conclusions:
- In this mortality cohort study, the authors estimated that there is evidence of an increased mortality from cancer but no increase in mortality from other causes amongst the exposed group of a chemical plant producing the intermediate benzoyl chloride.
- Executive summary:
Mortality rates were investigated among British workers exposed to benzotrichloride (98077), benzal-chloride (98873), benzyl-chloride (100447), and benzoyl-chloride (98884) at a factory that manufactured chlorinated toluenes.
The study population included 163 exposed and 790 unexposed factory workers employed for at least 6 months between 1961 and 1970. Death certificates were reviewed for the 91 subjects known to have died. Standardized Mortality Ratios (SMRs) were calculated using the mortality rates of the general population of England and Wales as comparison. A second analysis was performed using the Regression Models in Life Tables technique.
For all causes and for causes other than cancer, SMRs tended to increase with time since first employment. Elevated SMRs were found among the exposed group for all causes, allcancers, digestive system cancers, and respiratory system cancers. The unexposed group had elevated SMRs for cancers of the buccal cavity and throat. For both groups of workers combined, SMRs were increased for all causes and all cancers.
In the survival analysis using the Cox Proportional Hazards model, adjusting for age at entry to the survey and the time period when employment began, a statistically significant association between estimated cumulative exposure and deaths from cancer at all sites (but neither digestive nor respiratory cancers individually), was found for persons first employed before 1951.
The authors conclude that exposed workers employed before 1951 have an increased risk of cancer of the respiratory and digestive systems. Based on previous studies, they suggest that the most likely carcinogen is benzotrichoride.
As the authors mention it, cohort population design may have been unappropriate and introduce some bias in the experiment, furthermore the size of the cohorts has little statistical meaning. Besides, characterization of the exposure may have also introduce a bias as both categories (CT- and CT+) were subjective. Finally, no real measurement on exposure to benzoyl chloride is done and no specific results on it are available. Altogether, these parameters raise uncertainties on the conclusion of the impact of benzoyl chloride on workers. However, it gives little evidence and raises concerns on benzoyl chloride impacts on workers. The study is well documented and based on generally accepted scientific principles.
Therefore, considering all these elements, this study should be considered as valid with restrictions.
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