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EC number: 931-257-5 | CAS number: 68131-74-8
- 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
Endpoint summary
Administrative data
Description of key information
The test substances, Fluidized Bed Combustion (FBC) Bottom Ash and Fluidized Bed Combustion (FBC) Fly Ash, were tested for subchronic toxicity using the Method B.26 Sub-Chronic Oral Toxicity Test: Repeated Dose 90-day Oral Toxicity Study in Rodents, Council Regulation (EC) No. 440/2008, Published in O.J. L142, 2008.
No studies on repeated dose dermal toxicity and repeated dose inhalation toxicity of Fluidized Bed Combustion Ashes are available.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Dose descriptor:
- NOAEL
- 200 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
Additional information
Fluidized Bed Combustion (FBC) Fly Ash
The oral administration of the substance, Fluidized Bed Combustion (FBC) Fly Ash, to rats by gavage for a period of 90 consecutive days at dose levels 50, 200 and 800 mg/kg/day caused significant changes of haematological (haematocrit, haemoglobin, MCV, total leucocyte count, monocytes portion) and biochemical parameters (albumin, sodium). The urinalysis demonstrated effect of the test substance on properties of urine (pH, presence of leucocytes). The test substance had effect on microscopical structure of liver (focal fatty changes).
The value of NOAEL for MALES and FEMALES was established as 200 mg/kg/day.
Fluidized Bed Combustion (FBC) Bottom Ash
The oral administration of the substance, Fluidized Bed Combustion (FBC) Bottom Ash, to rats by gavage for a period of 90 consecutive days at dose levels 50, 200 and 800 mg/kg/day had effect on haematological parameters (differential leucocyte count, changes of red cell parameters, changes in haemocoagulation), water consumption and properties of urine (pH, presence of protein and leucocytes). The substance treatment had influence on liver (changes of some biochemical parameters, changes of macroscopical and microscopical structure of liver - vacuolation of hepatocytes).
The value of NOAEL for MALES is 200 mg/kg/day. The value of NOAEL for FEMALES is 800 mg/kg/day.
Changes observed after repeated dose oral exposure were similar in both Ashes. Absorption of (FBC) Ashes from the digestive system and their distribution throughout the body of experimental animals to relatively distant compartments was confirmed during oral repeated dose studies. Minerals and metals of (FBC) Ashes are absorbed largely in small intestine. No digestive tract irritation was noted.
No studies on repeated dose dermal toxicity and repeated dose inhalation toxicity of Fluidized Bed Combustion Ashes are available.
Repeated dose toxicity: via oral route - systemic effects (target organ) digestive: liver
Justification for classification or non-classification
The data from Study No. 65/09/8:Fluidized Bed Combustion (FBC) Fly Ash-Repeated Dose 90-day Oral Toxicity Study;VUOS-CETA Report No.: 10132, 2010 and from Study No. 66/09/8: Fluidized Bed Combustion (FBC) Bottom Ash - Repeated Dose 90-day Oral Toxicity Study; VUOS-CETA Report No.: 10133, 2010 are of acceptable quality for classification of substances for STOT RE.
The values of NOAEL was used in weight of evidence approach based on a comparison with classification criteria.
The Guidance Values (dose/concentration) for STOT RE Category 1 is C ≤ 10 mg/kg body weight/day, the Value Ranges (dose/concentration) for STOT RE Category 2 is 10 < C ≤ 100 mg/kg body weight/day for oral route exposure (Regulation (EC) No.1272/2008).
The lowest value of NOAEL (200 mg/kg body weight/day) is above the Guidance Values and Range (C).
Based on results of Repeated Dose 90-day Oral Toxicity Studies Fluidized Bed Combustion (FBC) Bottom Ash and Fluidized Bed Combustion (FBC) Fly Ash do not have to be classified as specific target organ toxicants following repeated exposure.
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.
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