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EC number: 215-693-7 | CAS number: 1344-37-2 This substance is identified in the Colour Index by Colour Index Constitution Number, C.I. 77603.
- 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:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: scientifically acceptable study
Data source
Reference
- Reference Type:
- publication
- Title:
- Mortalite par le cancer bronchopulmonaire dans une fabrique de pigments a base de chromates de plomb et de zinc
- Author:
- Haguenoer JM, Dubois G, Frimat P, Cantineau A, Lefrancois H and Furon D
- Year:
- 1 981
- Bibliographic source:
- Institut de Medecine du Travail, Faculte de Medecine - 59045 LILLE CEDEX - FRANCE
Materials and methods
- Study type:
- cohort study (prospective)
- Endpoint addressed:
- carcinogenicity
- Principles of method if other than guideline:
- Brochopulmonar cancer related mortality was evaluated in lead/zinc chromate pigment factory workers
- GLP compliance:
- no
Test material
- Reference substance name:
- Lead chromate
- EC Number:
- 231-846-0
- EC Name:
- Lead chromate
- Cas Number:
- 7758-97-6
- IUPAC Name:
- Lead Chromate
- Details on test material:
- - Analytical purity: no data
- Impurities (identity and concentrations): no data
- Composition of test material, percentage of components: no data
Constituent 1
Method
- Type of population:
- occupational
- Ethical approval:
- not specified
- Details on study design:
- HYPOTHESIS TESTED (if cohort or case control study): respiratory tract tumor deaths induced by the test material
METHOD OF DATA COLLECTION
- Type: recensement
STUDY PERIOD: Jan 1, 1958 - December 31 1977
STUDY POPULATION
- Total population (total no. of persons in cohort from which the subjects were drawn): 251 active workers during the study period (working in the factory at least for 6 months, starting before 1978 and still alive in 1958).
- Selection criteria: workers in the factory at least for 6 months, still alive in 1958 and having start the work in the plant before 1978.
- Sex/age/race: man
- Total number of subjects at end of study: 201
COMPARISON POPULATION
- Type: population of the department of North, France
- Details: statistics of the reference population were available (from 1958 to 1977), with the numbers of respiratory tract (non secondary tracheal, bronchial and pulmonar) tumor related, as well as total deaths, each 10 years.
HEALTH EFFECTS STUDIED
- Disease(s): respiratory tract tumor
- Diagnostic procedure: cytology and histology (Biopsy). - Exposure assessment:
- not specified
Results and discussion
- Results:
- EXPOSURE
- Average concentrations: could not be determined due to the changes (ameliorations) occurring progressively in the production.
INCIDENCE / CASES
- Incidence/ Number of cases for each disease / parameter under consideration: 30 (from a total of 50) deaths were attributable to pulmonary tumor (11), infarct (3), vasculocerabral accident (2), cerebral tumor (2), suicide (2), pulmonary acute edema (1), acute respiratory insufficiency (1), pancreatite (1), arterite (1), accident (1), intoxication (1), renal insufficiency (1), liver tumor (1), gastrointestinal tumor (2). The reason for the remaining deaths could not be determined. - Confounding factors:
- Zinc chromate was manufactured in the factory in parallel to lead chromate; azo and diazo dyes were additionally produced in the same factory up to 1965. It is therefore impossible to specifically incriminate the test substance.
Any other information on results incl. tables
The observed pulmonar tumors are summarized below:
Observation # | Year of birth | Exposition period (years) | Latency | Tobacco smoking | Diagnostic | Evolution period | Age at diagnostic |
1 | 1906 | 12.5 | 12.5 | + | 5 months | 56 | |
2 | 1907 | 17.5 | 17.75 | + | ganglion biopsy | 11 months | 59 |
3 | 1917 | 14 | 14.75 | + | cytology | 6 months | 51 |
4 | 1911 | 17.5 | 17.5 | + | bronchial biopsy | 6 months | 57 |
5 | 1925 | 23.5 | 23.5 | former smoker | bronchial biopsy | 1 year | 44 |
6 | 1925 | 20.25 | 20.25 | + | bronchial biopsy | 4 months | 46 |
7 | 1909 | 14.33 | 14.75 | - | 1 month | 63 | |
8 | 1918 | 2 | 15 | + | 1 year | 53 | |
9 | 1913 | 17.5 | 17.5 | + | bronchial biopsy | 34 months | 58 |
10 | 1929 | 18.75 | 18.33 | + | bronchial biopsy | 2 years | 43 |
11 | 1904 | 13.5 | 21 | + | cytology | 1 month | 71 |
12 | 1924 | 21.5 | 22.5 | + | bronchial biopsy | 6 months | 53 |
13 | 1914 | 19.33 | 18.75 | + | 19 months | 62 | |
14 | 1936 | 3 | 4.5 | + | bronchial biopsy | 1 month | 42 |
The incidence of deaths due to pulmonary tumor tripled in the control population during the 20 years of the study (310/13367 in 1958 vs. 797/14044 in 1977). Therefore, the comparison of the exposed group to the control population was made in a per year basis.
Based on the observations obtained from the control population the predicted number of deaths due to pulmonary tumor was 2.38 and was significantly lower than the 11 deaths in the exposed population (relative risk: 4.61). This is particularly important since the predicted 44.54 "normal" deaths (not due to pulmonary tumor or of unknown cause) compared to the actually observed 39 was not significant.
Lead poisoning was generally observed in 5 from 11 pulmonary tumor deaths. The urinary chrome levels were elevated in dried environment workers.
Applicant's summary and conclusion
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