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EC number: 617-779-3 | CAS number: 85940-94-9
- 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
Acute Toxicity: inhalation
Administrative data
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Well-conducted GLP study, according to guideline
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:
- 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)
- Deviations:
- no
- Principles of method if other than guideline:
- Not applicable
- GLP compliance:
- yes (incl. QA statement)
- Test type:
- standard acute method
- Limit test:
- no
Test material
- Reference substance name:
- Desmodur BL 3175
- IUPAC Name:
- Desmodur BL 3175
- Details on test material:
- - Name of test material (as cited in study report): Desmodur BL 3175
- Physical state: very viscous liquid
- NCO content: 0.04 %
- Composition: ca. 75 % polyisocyanurate blocked with 2-butanonoxime and ca. 25 % solventnaphtha 100
- Lot/batch No.: 214
- Storage condition of test material: room temperature, darkness
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Versuchstierzucht Winkelmann (Borchen, Germany)
- Strain: Bor: WISW (SPF-Cpb)
- Age at study initiation: 2-3 months
- Housing: 5 animals per cage
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 22 +/- 2
- Humidity (%): approx. 50
- Air changes (per hr): approx. 10
- Photoperiod (hrs dark / hrs light): 12 / 12
Administration / exposure
- Route of administration:
- inhalation: aerosol
- Type of inhalation exposure:
- nose/head only
- Vehicle:
- other: xylene
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: stainless steel inhalation chambers from Rhema Labortechnik (Hofheim, Germany)
- Exposure chamber volume: about 7 l
- Method of holding animals in test chamber: Plexiglas exposure tubes applying a directed-flow nose/head-only exposure principle
- Source and rate of air: compressed air was supplied by Boge compressors; about 86 air exchanges per hour
- Method of conditioning air: air was conditioned (i.e. freed from water, dust, and oil) automatically by a VIA compressed air dryer
- System of generating particulates/aerosols: with the help of a nozzle and conditioned compressed air a 75 % solution of the test substance in xylene up to a nominal concentration of 50000 µl/m3 air was nebulized in the pre-separator of the inhalation chamber
- Method of particle size determination: particle analyses were performed using a BERNER cascade impactor; the individual impactor stages were evaluated gravimetrically
- Treatment of exhaust air: the exhaust air was purified via cotton-wool filters; these filters were disposed of by Bayer AG
- Temperature, humidity: 20-22 °C, 18-50 % (rel. humidity)
TEST ATMOSPHERE
- Brief description of analytical method used: gravimetric analysis
- Samples taken from breathing zone: yes
VEHICLE
- Concentration of test material in vehicle (if applicable): 75 %
- Justification of choice of vehicle: due to the viscosity of the test item spraying as aerosol without addition of xylene was technically not possible
- Purity: no data
TEST ATMOSPHERE (if not tabulated)
- Particle size distribution: 82-99 % of particles were <= 5 µm
- MMAD (Mass median aerodynamic diameter) / GSD (Geometric st. dev.): MMAD: 2.25 µm (GSD: 2.06) for test conc. 2757 mg/m3 air - Analytical verification of test atmosphere concentrations:
- yes
- Duration of exposure:
- 4 h
- Concentrations:
- Mean analytical concentrations: 0, 343, 543, 1573 and 2757 mg/m3
- No. of animals per sex per dose:
- 5
- Control animals:
- yes
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: clinical signs were examined several times on the day of exposure and twice daily therafter; body weights were measured before exposure, on days 3 and 7, and weekly thereafter.
- Necropsy of survivors performed: yes
- Other examinations performed: reflexes - Statistics:
- Calculation of the LC50: If calculation of a median lethal concentration (LC50) is possible, it is performed by computer (HP 3000) according to the
method of AP. Rosiello, I.M. Essigmann, and G.N. Wogan (1977) as modified by Pauluhn (1983). This method is based on the maximurn-likelihood method of C.I. Bliss (1938).
Results and discussion
- Preliminary study:
- No data
Effect levels
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 2 757 mg/m³ air
- Exp. duration:
- 4 h
- Mortality:
- Aerosol concentrations up to 2757 mg/m3 air were tolerated without mortality (details see table 1).
LC50>1551 mg/m3 for the test substance which corresponds to 1396 mg/m3 or 1.396 mg/L when considering the respirable particules (<5µm). - Clinical signs:
- other: All animals exposed to 343 and 543 mg/m3 air of the test substance or to control group I (3334 µl xylene/m3 air) revealed no clinical signs. At 1573 mg/m3 air reduced motility, staggered gait, bradypnea and piloerection were observed. From the first post-
- Body weight:
- No effects on body weight were observed in the post-observation period at exposure concentrations of 343 mg/m3 air and above.
- Gross pathology:
- No indications of specific organ changes were seen in exposed animals compared to control groups.
- Other findings:
- No test substance-related changes on reflexes were observed between day 1 and day 3 of the post-observation period.
Any other information on results incl. tables
Table 1: Acute inhalation toxicity (aerosol) of Desmodur BL 3175
Sex | Analytical concentration (mg/m3) | Toxicological results | Onset and duration of signs | Particle <= 5 µm (%) |
male | 0 (control I *) |
0 / 0 / 5 |
--- | --- |
0 (control II **) | 0 / 5 / 5 |
4h - 6h | --- | |
343 | 0 / 0 / 5 |
--- | 97 |
|
543 | 0 / 0 / 5 |
--- | 99 |
|
1573 | 0 / 5 / 5 |
4h - 6h | 82 | |
2757 | 0 / 5 / 5 | 4h - 6h | 90 | |
female | 0 (control I *) | 0 / 0 / 5 |
--- | --- |
0 (control II **) | 0 / 5 / 5 | 4h - 6h | --- | |
343 | 0 / 0 / 5 | --- | 97 | |
543 | 0 / 0 / 5 | --- | 99 | |
1573 | 0 / 5 / 5 | 4h - 6h | 82 | |
2757 | 0 / 5 / 5 | 4h - 6h | 90 |
Toxicological results:
number of dead animals / number of animals with signs after cessation of exposure / number of animals exposed
* Control group I (3334 µl xylene / m3 air)
** Control group II (10000 µl xylene / m3 air)
Applicant's summary and conclusion
- Interpretation of results:
- not classified
- Remarks:
- Migrated information Criteria used for interpretation of results: EU
- Conclusions:
- Under the test conditions, DESMODUR BL 3175 is not classified for acute inhalation toxicity according to Annex VI to the Directive 67/548/EEC and
the CLP Regulation (EC) N°( 1272-2008). - Executive summary:
In an acute inhalation toxicity study, conducted according to OECD TG 403 guideline, in compliance with GLP, groups of Wistar rats (5 by sex) were exposed by inhalation route to Desmodur BL 3175 (75%) in xylene for 4 hours to nose/head only at aerosol concentrations of 0, 343, 543, 1573 and 2757 mg/m3. Animals were then observed for 14 days.
The inhalation LC50 in rats of both sexes was determined to be > 2757 mg/m3 air.
The maximum technically producible concentration was of 2757 mg/m3 which is below to the limit of classification (5 mg/L).
Moreover the vapor pressure of the test substance in Solvessonaphta 100 (75/25) is about 5hPa at 20°C which implies that the preparation is slightly volatile under normal conditions of use. This maximum technically producible concentration of 2757 mg/m3 air was tolerated without deaths and signs of toxicity.The observed symptoms are seen in a causal context with the used solvent xylene.
Therefore, according to Annex VI to the Directive 67/548/EEC and the CLP Regulation (EC) N°( 1272-2008), DESMODUR BL 3175 is not classified for acute inhalation toxicty.
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