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EC number: 231-152-8 | CAS number: 7440-43-9
- 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
Exposure related observations in humans: other data
Administrative data
- Endpoint:
- exposure-related observations in humans: other data
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 1998 to 1999
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study well documented, meets generally accepted scientific principles, acceptable for assessment.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- publication
- Title:
- Estimation of the Dietary Intake of Pesticide Residues, Lead, Cadmium, Arsenic and Radionuclides in France
- Author:
- Leblanc JC, Malmauret L, Guérin T, Bordet F, Boursier B and Verger P
- Year:
- 2 000
- Bibliographic source:
- Food. Addit. Contam. 17(11): 925-32
Materials and methods
- Type of study / information:
- Type of experience: Human - Exposure through Food
- Endpoint addressed:
- not applicable
- Principles of method if other than guideline:
- A study was conducted to assess the exposure to pesticide residues and other contaminants.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Cadmium
- EC Number:
- 231-152-8
- EC Name:
- Cadmium
- Cas Number:
- 7440-43-9
- Molecular formula:
- Cd
- IUPAC Name:
- cadmium
- Details on test material:
- - Name of test material (as cited in study report): 10 pesticides (omethoate, oxydemeton, phosalon, phosphamidon, triazophos, dicofol (op' + pp'), parathion ethyl, dichlorvos, procymidon and vinchlozolin), three heavy metals (lead, cadmium and arsenic) and three radionuclides (134caesium, 137caesium and 131iodine)
Constituent 1
Method
- Ethical approval:
- not specified
- Details on study design:
- - Taking into account seasonal variations, number of persons (between 10,000 and 20,000/day) and different population groups aged from 8 to 80 y old eating in different places (work place, school, university, hospital and retired person canteens), meal samples (breakfast and lunch) in duplicate were purchased in five areas throughout France, in 24 and 23 restaurants respectively during spring/summer 1998 and autumn/winter 1998/1999.
- Samples (solid and liquid parts, separately) were prepared, cooked and stored at -20°C prior to analysis
- Contaminants analysed: Samples were tested for the residues of 10 pesticides (omethoate, oxydemeton, phosalon, phosphamidon, triazophos, dicofol (op' + pp'), parathion ethyl, dichlorvos, procymidon and vinchlozolin), three heavy metals (lead, cadmium and arsenic) and three radionuclides (134caesium, 137caesium and 131iodine) - Exposure assessment:
- measured
- Details on exposure:
- none
Results and discussion
- Results:
- - Average cadmium content in lunch samples was 12 µg/kg with a maximum of 50 µg/kg.
- Average content in breakfast samples was 7 µg/kg with a maximum of 10 µg/kg.
- Average intake was then estimated at 7.5 µg/meal/person for lunch and at 2.4 µg/meat/person for breakfast. Average estimated daily intake was then calculated to be 17 µg/day/person.
- There were no significant differences according to location of the sampling or date of purchase.
Any other information on results incl. tables
- The average intake was estimated at 17 µg/day/person and represents 28% of the Provisional Tolerable Weekly Intake (Joint FAO/WHO Expert Committee on Food Additives 1993). It is lower than the intakes calculated by the Ministere de la Sante Publique et de l’ Assurance Maladie (1992) by the same method (23 µg/day/person), and by combining individual consumption and contamination data (20 µg/day/person) (Decloitre 1998).
- It can be noted that the most contaminated meals all contain spinach, kidney or seafood. The average intake, evaluated at 17 µg/day/person in this study is near the mean of those evaluated in other European countries (8-29 µg/ day/person), and similar to those published in(11-29 pig/day/person) (Urieta and Jalon 1999), and in(17 pig/day/person) (National Food Agency 1995). At the international level the range of the average intake, for a 60 kg adult, is between 11 µg/day in theand 57 µg/day in(European Commission 1996). These variations can be easily explained by the difference in dietary habits between countries. In particular, in the French diet, consumption of foods like spinach, seafood and offals, known to be highly contaminated by cadmium, can explain the variation. Reduction of cadmium contamination can be explained by good agriculture practice, which uses fertilizers low in cadmium and restricts disposal of sewage sludge on crop land.
Results of the analyses show that 53% of the data obtained for cadmium are above LOQ
Table: Distribution of the intake of heavy metals of the Lunch and breakfeast meals (solid + liquid part, n=1O3, data <LOQ=LOQ).
-------------------------------------------------------
Cadmium (µg/meal)
Breakfast (n=10)
Maximum 4.0
97.5th percentile 3.9
Mean 2.4
Median 2.1
Minimum 1.5
SD 0.7
Lunch (n=93)
Maximum 32.0
97.5th percentile 26.4
Mean 7.5
Median 5.4
Minimum 2.6
SD 5.9
-------------------------------------------------------
Applicant's summary and conclusion
- Conclusions:
- The average cadmium content in lunch and dinner samples was calculated to be 12 µg/kg (maximum: 50 µg/kg) and 7 µg/kg (maximum: 10 µg/kg), respectively. The average intake for lunch and breakfast was calculated to be 7.5 and 2.4 µg/meat/person, respectively. Average estimated daily intake was then calculated to be 17 µg/day/person. Moreover, there were no significant differences according to location of the sampling or date of purchase.
- Executive summary:
A study was conducted to assess the exposure to pesticide residues and other contaminants.
Taking into account seasonal variations, number of persons (between 10,000 and 20,000/day) and different population groups aged from 8 to 80 y old eating in different places (work place, school, university, hospital and retired person canteens), meal samples (breakfast and lunch) in duplicate were purchased in five areas throughout France, in 24 and 23 restaurants respectively during spring/summer 1998 and autumn/winter 1998/1999. Samples (solid and liquid parts, separately) were prepared, cooked and tested for the residues of 10 pesticides (omethoate, oxydemeton, phosalon, phosphamidon, triazophos, dicofol (op' + pp'), parathion ethyl, dichlorvos, procymidon and vinchlozolin), three heavy metals (lead, cadmium and arsenic) and three radionuclides (134caesium, 137caesium and 131iodine).
The average cadmium content in lunch and dinner samples was calculated to be 12 µg/kg (maximum: 50 µg/kg) and 7 µg/kg (maximum: 10 µg/kg), respectively. The average intake for lunch and breakfast was calculated to be 7.5 and 2.4 µg/meat/person, respectively. Average estimated daily intake was then calculated to be 17 µg/day/person. Moreover, there were no significant differences according to location of the sampling or date of purchase.
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