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EC number: 265-477-1 | CAS number: 65122-06-7
- 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:
- other: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- other information
- Study period:
- from March 26 to April 12, 1990
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Source study has reliability 1; details on the read-across approach are attached in section 13.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 990
- Report date:
- 1990
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- Version / remarks:
- 1981
- GLP compliance:
- yes
- Test type:
- standard acute method
- Limit test:
- no
Test material
- Reference substance name:
- Similar Substance 01
- IUPAC Name:
- Similar Substance 01
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: 2 -3 months.
- Weight at study initiation: 180 - 210 g.
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: 5 days
ENVIRONMENTAL CONDITIONS
- Temperature: 22 ± 2 °C.
- Humidity: ca. 50 %.
- Air changes: 10 per hr.
- Photoperiod: 12 h light / 12 h dark.
Administration / exposure
- Route of administration:
- other: inhalation of aerosol or dust
- Type of inhalation exposure:
- nose/head only
- Vehicle:
- other: water (aerosol)
- Details on inhalation exposure:
- CHAMBER DESCRIPTION
- exposure chamber volume: ca. 20 l
- air: compressed air at 8 - 10 bar
- method of conditioning air: removal of water, dust and oil
GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION: aerosol
- exposure apparatus: inhalation chamber with pre-separator.
- aerosol generation: with nozzle and conditioned compressed air (10 l of air per minute, dispersion pressure 500 kPa). 500000 µl/m3 of air of 12 % aqueous dilution were nebulised under dynamic conditions in the pre-separator of the inhalation chamber. Container with the aqueous test sample dilution was continuously stirred using a magnetic stirrer. The solution was transferred using a peristaltic pump into the nozzle.
- control of particle size: pre-separator increases efficiency of aerosol generation and also allows deposition of larger particles.
- air exchange: 30 times per hour.
- equilibrium: reached in 6 minutes.
- treatment of exhaust air: 80 % through cotton-wool filter (aerosol filter).
GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION: dust
- exposure apparatus: inhalation chamber without pre-separator.
- system of generating particulates: dust generated by 'Exactomat 4200'.
- air supply: 28 l/min.
- air discharged: 20 l/min.
- air exchange: 84 times per hour.
- equilibrium: reached in 6 minutes.
- treatment of exhaust air: absolute filter.
TEST ATMOSPHERE
- dust temperature and humidity: ca 22 °C and 20 - 30 %.
- aerosol temperature and humidity: ca 23 °C and > 90 %.
- temperature and humidity in air chamber: measured every 10 minutes.
- reference group: exposure 6 h/day for 5 days.
- test group: 4/h exposure.
- brief description of analytical method used: a humidity sensor was used in which a water-attracting polymer serves as a dielectric. As a function of the moisture content of the ambient, air penetrates into water as polymer and causes a large change in the capacitance of the capacitor. The moisture measuring cell is protected by a Teflon membrane against aerosols and dust particles. The calibration of the sensors is wet with saturated salt solutions. The calibration of the temperature sensors was carried out with a standard thermometer.
ANALITICS OF TEST ATMOSPHERE : aerosol
- nominal concentration calculated from the ratio of the sprayed into the pre-separator of the inhalation chamber test sample (mg) and the total air flow rate per inhalation chamber (m3). The analytical lower concentrations - as compared to the nominal concentrations - attributed to the deposition of large particles in the pre-separator. The determination of the actual specimen concentration in the breathing zone of rats was performed with the help of filter analyses dried on gravimetric determination. 10-20 l of air in the test atmosphere breathing region of the rats were removed with a flow of 4 l/min per analysis.
- aerosol distribution: adequate to expose all potential target structures of the respiratory tract.
ANALITICS OF TEST ATMOSPHERE: dust
- indication of a nominal concentration reading is not possible for technical reasons. Determination of the actual sample concentration in the breathing zone of rats was performed with the help of filter analyses evaluated gravimetrically.
- particles features: sampling for analysis of particle distribution was carried out in the immediate breathing zone of rats. The individual impactor stages were evaluated gravimetrically.
- particle size distribution: adequate to expose all potential target structures of the respiratory tract. - Analytical verification of test atmosphere concentrations:
- yes
- Duration of exposure:
- 4 h
- Concentrations:
- Analytic concentration of dust: 943 and 5070 mg/m3 air.
Analytic concentration of aerosol: 1075 mg/m3 air.
Nominal concentration of aerosol: 60000 mg/m3 air. - No. of animals per sex per dose:
- 5 animal/sex/dose.
- Control animals:
- yes
- Details on study design:
- - Duration of observation period following administration: 14 days.
- Frequency of observations and weighing: daily.
- Necropsy of survivors performed: yes.
- Other symptoms considered in animal assessment: respiration, circulation, mucous membranes of eyes and respiratory tract, condition of snout skin and ears, coat condition, cleaning activities, somatomotor and behaviour patterns, central nervous system. - Statistics:
- Pairwise Fisher's Test and Chi-Square-Test.
Results and discussion
Effect levelsopen allclose all
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 5 070 mg/m³ air (analytical)
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Remarks on result:
- other: dust
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 3 245 mg/m³ air (analytical)
- Based on:
- act. ingr.
- Exp. duration:
- 4 h
- Remarks on result:
- other: dust
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 1 075 mg/m³ air (analytical)
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Remarks on result:
- other: aerosol
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 688 mg/m³ air (analytical)
- Based on:
- act. ingr.
- Exp. duration:
- 4 h
- Remarks on result:
- other: aerosol
- Mortality:
- Dust and aerosol exposure: no mortality up to the highest doses.
- Body weight:
- Dust exposure: significant difference only in group 3 (5070 mg/m3 air).
Aerosol exposure: significant difference only in group 2 (1075 mg/m3 air). - Gross pathology:
- Dust and aerosol exposure: no evidence of specific organ changes.
Any other information on results incl. tables
Dust exposure
The analysis of the particle size distribution of the dust in the breathing zone of the rats did not produce adequate respirable mass fraction .
Group 1 (control): all rats
tolerated the treatment clinically asymptomatic.
Group
2 and 3 (943 and 5070 mg/m3air): dyspnea, respiratory sounds,
slow and difficult breathing, decreased motility, laxity, serous nasal
discharge and unkempt fur.
Qualitative differences between group 2 and 3 were not evident. With regard to the duration of symptoms, however, a concentration dependency was seen. Group 3 rats showed strong respiratory tract irritation.
The relatively rapid reversibility of respiratory tract irritation, the overall low inhalability of dust and the only slightly pronounced concentration dependence lead to the conclusion that the irritation is induced by a particle deposition in the upper respiratory tract or in the nose and throat.
group | sex | no. animals | conc. mg/m3 air | dead animals | animals with symptoms | symptom duration | % particles ≤ 3 µm |
1 | M | 5 | 0 | 0 | 0 | - | - |
2 | M | 5 | 943 | 0 | 5 | 4h - 1d | 4 |
3 | M | 5 | 5070 | 0 | 5 | 4h - 2d | 1 |
1 | F | 5 | 0 | 0 | 0 | - | - |
2 | F | 5 | 943 | 0 | 5 | 4h - 2d | 4 |
3 | F | 5 | 5070 | 0 | 5 | 4h - 2d | 1 |
Aerosol exposure
The analysis of the particle size distribution of the aerosol in the breathing zone of the rats revealed a high inhalable mass fraction.
Group 1 (control): all rats tolerated the treatment clinically asymtomatic.
Group 2 (1075 mg/m3air): slow and difficult breathing, reduced motility, unkempt and ruffled fur.
group | sex | no. animals | conc. mg/m3 air | dead animals | animals with symptoms | symptom duration | % particles ≤ 3 µm |
1 | M | 5 | 0 | 0 | 0 | - | - |
2 | M | 5 | 1075 | 0 | 5 | 4h - 5d | 61 |
1 | F | 5 | 0 | 0 | 0 | - | - |
2 | F | 5 | 1075 | 0 | 5 | 4h - 3d | 61 |
Applicant's summary and conclusion
- Interpretation of results:
- study cannot be used for classification
- Remarks:
- no mortality up to the highest tested doses, which are below the threshold for classification within the CLP Regulation (EC 1272/2008)
- Conclusions:
- Overall, dust and aerosol exposure showed that, via the respiratory tract, particles had no particular acute inhalation toxicity. Indeed, no mortalities were recorded up to the highest tested doses. Thus, LD50 > 1075 and 5070 mg/m3 air for aerosol and dust respectively.
However, high concentrations of particulate material, as dust, may cause respiratory tract irritation due to physical properties of the dust, which dries the mucous membranes of the upper respiratory tract. - Executive summary:
Method
Acute toxicity by inhalation of dust particles or aerosol in male and female rats with a 14 -day observation period.
Results
No mortalilty was recorded up to the highest tested concentrations, namely 5070 mg/m3 air as dust and 1075 mg/m3 air as aerosol, i.e. 3245 and 688 mg active ingredient/m3 air . Accordingly, no LC50 could be identified.
A large fraction of aerosol particles is respirable, while upon dust exposure, irritation of the respiratory tract was seen.
Symptoms, as slow/difficult breathing and reduced motility, were reversible under test conditions, with duration depending on physical form (dust or aerosol) of the substance, concentration of the substance and sex of animals.
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