Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 240-383-3 | CAS number: 16291-96-6 An amorphous form of carbon produced by partially burning or oxidizing wood or other organic matter.
- 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

Acute Toxicity: inhalation
Administrative data
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2010-09-24 to 2010-10-09
- Reliability:
- 1 (reliable without restriction)
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.2 (Acute Toxicity (Inhalation))
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.1300 (Acute inhalation toxicity)
- Deviations:
- no
- Principles of method if other than guideline:
- no aplicable
- GLP compliance:
- no
- Test type:
- standard acute method
- Limit test:
- yes
Test material
- Reference substance name:
- Charcoal
- EC Number:
- 240-383-3
- EC Name:
- Charcoal
- Cas Number:
- 16291-96-6
- IUPAC Name:
- Carbón vegetal
- Details on test material:
- Batch no.: 29004
Appearance: charcoal typic
Purity: C-Fix: 80.5%; dose calculation not adjusted to purity
Expiry: December 2030
Storage condition: At room temperature, moisture protected
Safety precautions: Routine hygienic procedures
The test atmosphere was generated from the micronized powder of test item as supplied by the Sponsor. No vehicle was used.
The original test item was micronized by mill (Fritsch, Laborette, Lot. 09.203.381) to around 150 µm. This particle size was used in the test. The actual particle size distribution in the breathing zone was determined by the parameters of the aerosol generation system employed.
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: CRL (WI) BR of Wistar origin
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- Source: Toxi-Coop Zrt. 1103 Budapest, Cserkesz u. 90.
Hygienic level: SPF at arrival and kept in good conventional environment during the study.
Age of animals: Young adult rats, 8-12 weeks old
Body weight range at treatment: males: 314-345 g, female: 217-243 g
Number of animals: 5 male and 5 female (nulliparous and non pregnant animals) rats
Number of animals/group: 5 animals/ sex
Acclimatisation time: 15 d
Acclimatisation to the test apparatus: 4 d
Individual identification was performed by numbers on the tail of the animals written with a permanent marker. The numbers were given on the basis of the laboratory master file of the testing laboratory and were remarked as necessary to ensure the correct identification.
The cages were marked by cards holding information about study number, sex of animals, dose group, cage number and individual animal numbers.
All animals were sorted according to body weight by computer and grouped according to weight ranges. There were an equal number of animals from each weight group in each of the experimental groups during the randomisation.
Animal health: Only healthy animals were used for the study. Healthy status was certified by the breeder.
Housing: Group caging (2 or 3 animals, by sex, per cage)
Cage type: Type II polypropylene/polycarbonate.
Bedding: Certified laboratory wood bedding (Lignocel Hygienic Animal Bedding produced by J. Rettenmaier & Söhne GmbH+Co.KG; D-73494 Rosenberg Holzmühle 1, Germany). The cages and bedding were changed twice a week.
Illumination: Artificial light, from 6 a.m. to 6 p.m.
Temperature: 22±3 °C
Relative humidity: 30-70 %
Ventilation: 8-12 air exchanges/hour by central air-condition system.
Environmental conditions were maintained by an air-condition system. Temperature and relative humidity were verified and recorded daily during the study.
The animals received ssniff® SM R/M-Z+H complete diet (ssniff Spezialdiäten GmbH, D-59494 Soest, Germany) ad libitum and tap water from watering bottles.
The food and water are considered not to contain any contaminants that could reasonably be expected to affect the purpose or integrity of the study. The food supplier provided an analytical certificate of the standard diet for the batch used. The drinking water is periodically analysed.
Administration / exposure
- Route of administration:
- inhalation: dust
- Type of inhalation exposure:
- nose only
- Vehicle:
- air
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: Anodised aluminium Flow Past Exposure Chamber (CR Equipment SA, Switzerland)
- Exposure chamber volume:
- Method of holding animals in test chamber: The animals were held in polycarbonate restraining tubes and exposed “nose-only” under dynamic air flow conditions. The animals were distributed in two levels of the exposure chamber.
- Source and rate of air: The air was supplied by an oil-free air compressor and was filtered in a two-stage filter set. The temperature of the air was regulated by a heat exchanger. The airflow rate to each animal port was 1.0 L/min.
- System of generating particulates/aerosols:
The test atmosphere was generated by the compressed air dry powder dispersion technique at the pressure of 5 bar. The test item was compacted in the container of the aerosol generator type Wright (TSE Systems GmbH, Bad Homburg, Germany) by the pressure of approximately 1.5 ton/cm². An abrasive disc was used to supply the test item particles into the dispersing tube (diameter: 2.4mm, length: 150mm). The proportion of large particles was decreased by implementing in the system an impactor- and a cyclone-type micronizer/size-selector (TSE Systems GmbH, Bad Homburg, Germany). Constancy of particle size distribution was determined by performing multiple particle size analyses during characterization using a cascade impactor.
- Method of particle size determination: See section "any other information on materials and methods incl. tables".
- Temperature, humidity, pressure in air chamber: Temperature: 20.3–23.3°C, relative humidity: 40.3–62.6%
TEST ATMOSPHERE
- Brief description of analytical method used: See section "Analytical verification of test atmosphere concentrations"
TEST ATMOSPHERE
- Particle size distribution: Inhalable fraction (< 4 µm): 52.3%
- MMAD (Mass median aerodynamic diameter) / GSD (Geometric st. dev.): 3.523 µm / 2.46 - Analytical verification of test atmosphere concentrations:
- yes
- Remarks:
- The actual concentration of generated atmosphere was measured gravimetrically at regular intervals (about 50-60 min) during exposure by pulling a volume of 4 L of test atmosphere from the exposure chamber through glass fibre filters Fiberfilm T60A20
- Duration of exposure:
- ca. 4 h
- Concentrations:
- Mean achieved concentration: 4.968 mg/L
- No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 d
- Frequency of observations and weighing:
Animals were checked twice daily during the 14-d observation period for morbidity and/or mortality.
All animals were observed for clinical signs at 1st, 2nd and 3rd hours during exposure, as soon as practicable following removal from restraint, 1 h after exposure and subsequently once daily for 14 d.
Individual bodyweights were recorded on the day of exposure prior to exposure (Day 0) and on Days 1, 3, 7 and 14.
- Necropsy of survivors performed: yes
- Other examinations performed: clinical signs, body weight,organ weights, histopathology, - Statistics:
- No statistical evaluation was performed.
Results and discussion
- Preliminary study:
- A sighting exposure was performed with a test item concentration of 5 mg/L on a single male and female animal. Animals were exposed for 4 h. The achieved average concentration of the test atmosphere was 4.7 mg/L, determined by gravimetry and aerosol light scattering photometer. In the breathing zone the MMAD of the dust particles was 3.48 μm. Both animals survived the treatment and the following 72 h.
Effect levels
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 4.97 mg/L air
- Exp. duration:
- 4 h
- Mortality:
- No animal died during the study.
- Clinical signs:
- other: All animals were observed for clinical signs at the 1st, 2nd and 3rd hour during exposure, as soon as practicable following removal from restraint, 1 h after exposure and subsequently once daily for 14 d. Individual clinical observations are presented in
- Body weight:
- Individual bodyweights were recorded on the day of exposure Day 0 (prior to exposure) and Days 1, 3, 7 and 14.
In both genders, body weight loss was observable on the day of inhalation exposure. In both sexes, a compensation of body weight loss was found from the 3rd day of the observation period onwards.
On basis of body weight and body weight gain data, there was no notable test item effect observable in the exposed animals. - Gross pathology:
- At the end of the 14-d observation period, the animals were euthanized by exsanguination under anaesthesia and gross necropsies were performed. These included a detailed examination of the abdominal and thoracic cavities with special attention given to the respiratory tract for macroscopic signs of irritancy or local toxicity.
Greyish mottled lungs and grey-coloured peribronchial lymph nodes were observed in the test animals, which may be related to test item but do not have any toxicological relevance. - Other findings:
- Deposition of brown-black particles in the lumen of alveoli and in the interstitium were detectable in the investigated lungs, in connection with the macroscopically observable discoloration of the organ.
The localisation of these particles were mainly extracellular but some particles were phagocytized by alveolar macrophages. No particles were visible on the ciliated epithelium of the airways in the bronchial region, trachea or nasal mucosa.
No inflammatory infiltrates, oedema, accumulation of alveolar macrophages or accumulation of phospholipids in alveoli (alveolar proteinosis or lipoproteinosis) was detectable. Hypertrophy or hyperplasia of type II cells in the alveoli was not observed as well.
Deposition of brown-black particles in the sinusoidal lumen of peribronchial lymph nodes was observed, too. No any degenerative, inflammatory or other lesion with toxicological significance in the lymph nodes was detected.
Applicant's summary and conclusion
- Interpretation of results:
- practically nontoxic
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- Deposition of brown-black particles in the lumen of alveoli and in the interstitium were detectable in the investigated lungs, in connection with the macroscopically observable discoloration of the organ.
The localisation of these particles were mainly extracellular but some particles were phagocytized by alveolar macrophages. No particles were visible on the ciliated epithelium of the airways in the bronchial region, trachea or nasal mucosa.
No inflammatory infiltrates, oedema, accumulation of alveolar macrophages or accumulation of phospholipids in alveoli (alveolar proteinosis or lipoproteinosis) was detectable. Hypertrophy or hyperplasia of type II cells in the alveoli was not observed as well.
Deposition of brown-black particles in the sinusoidal lumen of peribronchial lymph nodes was observed, too. No any degenerative, inflammatory or other lesion with toxicological significance in the lymph nodes was detected.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.