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EC number: 266-006-2 | CAS number: 65996-73-8 The wetted particulate matter recovered by wet collection techniques, including pollution abatement equipment, for the recovery of materials such as iron sinter dust, blast furnace dust, steelmaking dust, and mill scale.
- 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
Key value for chemical safety assessment
Skin sensitisation
Link to relevant study records
- Endpoint:
- skin sensitisation: in vivo (LLNA)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2.2.2010-16.2.2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.42 (Skin Sensitisation: Local Lymph Node Assay)
- Deviations:
- no
- GLP compliance:
- yes
- Type of study:
- mouse local lymph node assay (LLNA)
- Species:
- mouse
- Strain:
- Balb/c
- Sex:
- female
- Details on test animals and environmental conditions:
- TEST ANIMALS
- Source: breeding farm VELAZ, s.r.o., Kolec u Kladna, Czech Republic
- Age at study initiation: 8-10 weeks
- Weight at study initiation: 19.4-22.6 g
- Housing: group-wise five in macrolon cageswith sterilized softwood shavings, cleaning and disinfection of animal room was regularly performed (according to SOP No. 10)
- Diet (e.g. ad libitum): pelleted standard diet for experimental animals ad libitum
- Water (e.g. ad libitum): drinking tap water ad libitum (water quality corresponded to Ministerial Decree No. 252/2004 Czech Coll of Law)
- Acclimation period: 5 days at least
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22±3°C (permanently monitored)
- Humidity (%): 30-70 % (permanently monitored)
- Photoperiod (hrs dark / hrs light): 12 hours light/dark cycle - Vehicle:
- other: DAE 433: dimethylacetamide (40 %), acetone (30 %), ethanol (30 %)
- Concentration:
- 30% (w/v) (300 mg/ml)
3% (w/v) (30 mg/ml)
0.3% (w/v) (3 mg/ml) - No. of animals per dose:
- 5 animals/dose
- Details on study design:
- MAIN STUDY
Experimental schedule:
Day 1:
Open application of 25 µl (in the morning, by pipette) of appropriate emulsions of the test substance, the vehicle alone or the positive control to the dorsum of each ear.
Days 2 and 3:
The application procedure repeated as carried out on day 1.
Days 4 and 5:
No treatment.
Day 6:
Injection of 250 µl of phosphate-buffered saline (PBS) containing 7.1 x105 Bq of 3H-methyl thymidine into all test and control mice via the tail vein. Five hours later, the animals were killed.
PILOT TEST
The highest test-substance concentration of 30% was administered to three animals to assess possible systemic toxicity. During the pilot experiment clinical symptoms of systemic toxicity were not observed. No macroscopic changes (after necropsy) were found in all three animals.
TREATMENT PREPARATION AND ADMINISTRATION:
Application:
The volume of the dose was constant for all groups of animals - 25 µl of the appropriate dilution to the dorsum of each ear once a day morning for 3 consecutive days. The application was performed very slowly by micropipette to avoid losses caused by draining from the ear.
Preparation for administration: All emulsions were prepared by suspending an appropriate amount of Slimes and Sludges, blast furnace and steelmaking in the vehicle to obtain a concentration of 30%, 3% or 0.3% (w/v). The emulsions were prepared before the start of application by mixing on magnetic stirrer and were still being mixed during application.
Frequency of preparation: Each day of administration - Positive control substance(s):
- other: 1-chloro-2,4-dinitrobenzene
- Statistics:
- For statistical calculations the software Statgraphic(R) Centurion (version XV, USA) was used. At first the global comparison of all three values of the concentration groups with vehicle control is performed by applying the non-parametric Kruskal-Wallis test, and then the non-parametric two-group Mann-Whitney rank test (probability level 0.05) was applied to all two-group comparisons.
- Positive control results:
- see Table 1
- Key result
- Parameter:
- SI
- Value:
- 1.52
- Test group / Remarks:
- 0.3 %
- Key result
- Parameter:
- SI
- Value:
- 1.29
- Test group / Remarks:
- 3 %
- Key result
- Parameter:
- SI
- Value:
- 1.59
- Test group / Remarks:
- 30 %
- Interpretation of results:
- not sensitising
- Remarks:
- Migrated information
- Conclusions:
- The test substance Slimes and Sludges, blast furnace and steelmaking had a negative result in LLNA test.
- Executive summary:
The test substance, Slimes and Sludges, blast furnace and steelmaking, was tested for the assessment ofskin sensitisation potential with the murine local lymph node assay. This study is a part of the test substance health hazard evaluation.
The Local Lymph Node Assay (LLNA) with radionuclide was used. The testing was conducted according to the EU Method B.42, Skin sensitization: Local Lymph Node Assay, Council Regulation (EC) No. 440/2008, published in O.J. L142, 2008.
In this study the contact allergenic potential of Slimes and Sludges, blast furnace and steelmaking was evaluated after topical application to female BALB/c mice. Five mice per group were exposed on the dorsum of both ears by test and control substances once a day during 3 consecutive days. Primary proliferation of lymphocytes in the lymph node draining the site of application was evaluated by using radioactive labelling. The ratio of the proliferation in treated groups to that in vehicle controls, termed the Stimulation Index (SI), was determined.
Concentrations: positive control DNCB (2,4-dinitrochlorobenzene): 0.5% (w/v) and Slimes and Sludges, blast furnace and steelmaking: 30%, 3%, 0.3% (w/v) in the solvent mixture, DAE 433.
The animals exposed to the test substance at all dose levels showed no pathological skin reactions. No clinical symptoms of intoxication throughout the experiment were observed at the all dose levels. There was no significant difference in body weight increment of treated groups in comparison to the vehicle control.
The positive control substance DNCB elicited a reaction pattern with statistically significant increase in cell proliferation, the Stimulation Index reaching 16.94, which was consistent with its expected mode of action as a contact allergen.
The comparison of the Stimulation Indexes between the treated groups and the control group revealed that the test substance Slimes and Sludges, blast furnace and steelmaking did not cause a significant increase in radioisotope incorporation into the DNA of dividing lymphocytes. This effect was dose dependent. The maximal SI was 1.59 at the highest test concentration of 30 %.
The test substance Slimes and Sludges, blast furnace and steelmaking had anegative result in LLNA test.
Based on these results the test substance, Slimes and Sludges, blast furnace and steelmaking, does not have to be classified as the substance, which may cause sensitisation by skin contact.
Reference
Table 1: Cell suspensions radioactivity
Group | Radioisotope incorporation in lymph nodes | |
Mean DPM | stimulation index | |
negative control | 237.26 | 1.00 |
positive control | 4018.42 | 16.94 |
30% | 377.19 | 1.59 |
3% | 305.17 | 1.29 |
0.3% | 359.65 | 1.52 |
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed (not sensitising)
- Additional information:
The Local Lymph Node Assay (LLNA) with radionuclides was used. The testing was conducted according to the EU Method B.42, Skin sensitization: Local Lymph Node Assay. The test substance Slimes and Sludges had a negative result in the LLNA test.
The test substance Slimes and Sludges does not be qualified as skin sensitizing.
Respiratory sensitisation
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
The test substance Slimes and Sludges does not be qualified as skin sensitizing.
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