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EC number: 939-478-9 | CAS number: -
- 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:
- 03 October 2016 - 17 October 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- The study was performed as a data requirement for a registration in China.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 017
- Report date:
- 2017
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 403 (Acute Inhalation Toxicity)
- Version / remarks:
- September 2009
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.2 (Acute Toxicity (Inhalation))
- Version / remarks:
- May 2008, including most recent amendments
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.1300 (Acute inhalation toxicity)
- Version / remarks:
- August 1998
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: Japanese Ministry of Agriculture, Forestry and Fisheries (JMAFF), 12 Nousan, Notification No 8147
- Version / remarks:
- November 2000; including the most recent partial revisions
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- d.d. 03 November 2015
- Test type:
- fixed concentration procedure
- Limit test:
- yes
Test material
- Reference substance name:
- -
- EC Number:
- 420-990-1
- EC Name:
- -
- Cas Number:
- 146421-65-0
- Molecular formula:
- C20H36N2O6
- IUPAC Name:
- 4-(ethenyloxy)butyl N-[6-({[4-(ethenyloxy)butoxy]carbonyl}amino)hexyl]carbamate
- Reference substance name:
- 4-(ethenyloxy)butyl N-{6-[({[6-({[6-({[4-(ethenyloxy)butoxy]carbonyl}amino)hexyl]carbamoyl}oxy)hexyl]oxy}carbonyl)amino]hexyl}carbamate
- Cas Number:
- 1516571-16-6
- Molecular formula:
- C34H62N4O10
- IUPAC Name:
- 4-(ethenyloxy)butyl N-{6-[({[6-({[6-({[4-(ethenyloxy)butoxy]carbonyl}amino)hexyl]carbamoyl}oxy)hexyl]oxy}carbonyl)amino]hexyl}carbamate
- Test material form:
- solid: flakes
- Details on test material:
- Appearance: White flakes
Name as cited in test report: URALAC P 1920C
Test item storage: At room temperature
Constituent 1
Constituent 2
Test animals
- Species:
- rat
- Strain:
- other: Crl: WI(Han)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Deutschland, Sulzfeld, Germany
- Females nulliparous and non-pregnant: yes
- Age at study initiation: 10-11 weeks old
- Weight at study initiation: males: 293-314 g; females: 193-211 g
- Fasting period before study: no
- Housing: Group housing of 5 animals in Makrolon cages (type IV; height 18 cm) containing sterilised sawdust as bedding material and paper as cage-enrichment
- Diet: pelleted rodent diet (SM R/M-Z from SSNIFF® Spezialdiäten GmbH, Soest, Germany), ad libitum except during exposure to the test item
- Water: tap water ad libitum except during exposure to the test item
- Acclimation period: 5 days
Diet, water, bedding and cage enrichment evaluation for contaminants and/or nutrients was performed according to facility standard procedures. There were no findings that could interfere with the study.
ENVIRONMENTAL CONDITIONS (set to maintain)
- Temperature (°C): 18 - 24
- Humidity (%): 40-70
- Air changes (per hr): at least 10
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- inhalation: aerosol
- Type of inhalation exposure:
- nose only
- Vehicle:
- air
- Mass median aerodynamic diameter (MMAD):
- > 3.8 - < 5.2 µm
- Geometric standard deviation (GSD):
- 1.8
- Remark on MMAD/GSD:
- The Mass Median Aerodynamic Diameter (MMAD) and geometric standard deviation (gsd) were determined twice during the exposure period. The MMAD was 5.2 μm (gsd 1.8) and 3.8 μm (gsd 1.8). The first measurement just felt outside the recommended range of 1 - 4 μm. There was no evidence for test item deposition in the upper airways due to this larger MMAD. Since the second measurement felt within the recommended range and since it is generally known that good distribution throughout the lung requires particles with an aerodynamic diameter between 1 and 5 μm, it can be assumed that sufficient deposition in the lower respiratory tract occurred during the exposure.
- Details on inhalation exposure:
- TEST ITEM PREPARATION:
Before use the test item was grinded with an automatic grinder (Retsch PM100 Planetary Ball Mill, Retsch GmbH, Haan, Germany) and additionally with a small automatic grinder. The test item was passed through a 250 μm steel mesh sieve before use.
GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: exposure chamber based on the directed flow nose only inhalation chamber (Am. Ind. Hyg Assoc. J. 44(12): 923-928, 1983)
- Exposure chamber volume: ca. 150 mL
- Test chamber: polycarbonate restraining tubes
- Source and rate of air: at least 1 L/min (theoretical air flow in each animal port).
- System of generating aerosols: The test item was fed to a stream of pressurized air (mean air flow 11 L/min) by means of a spiral feeder (Randcastle Extrusion Systems, Cedar Grove, NJ, USA) and a micronizing jet mill (Bernstein, D.N., Aerosols, pp 721- 723, 1984). The aerosol was passed through a series of three cyclones, allowing larger particles to settle, before it entered the exposure chamber.
From the exposure chamber the test atmosphere was passed through a filter before it was released to the exhaust of the fume hood.
- Method of particle size determination: The particle size distribution was characterized twice during the exposure period. The samples were drawn (2 L/min) from the test atmosphere through a tube mounted in one of the free animal ports. The samples were collected with an 8 stage Marple personal cascade impactor containing fiber glass filters and a fiber glass back-up filter. Amounts of test item collected were measured gravimetrically. Subsequently the Mass Median Aerodynamic Diameter (MMAD) and the Geometric Standard Deviation (GSD) were determined.
- System stability: An indication of the stability of the test atmosphere was obtained from the concentration measurements, which were equally distributed over time.
- Temperature and humidity in air chamber: 21.1-21.6 °C and 54-60% respectively
TEST ATMOSPHERE
- Brief description of analytical method used: Samples were drawn from the test atmosphere through a tube mounted in one of the free animal ports of the middle section of the exposure chamber. Samples were drawn through a glass fiber filter. The collected amount of the test item in the air sample was measured gravimetrically. Sample volumes were measured by means of a dry gas meter. The time-weighted mean concentration with the standard deviation was calculated.
- Samples taken from breathing zone: Yes, the actual concentration was determined twenty-one times during the exposure period.
- The temperature and relative humidity were measured with a humidity and temperature indicator (E+E Elektronik, Engerwitzdorf, Austria) and were recorded after the animals were placed in the experimental set-up and at 30 minute intervals after initiation of the exposure.
CLASS METHOD
- Rationale for the selection of the starting concentration: Target concentrations were based on the cut off concentration values specified in the UN and EC classification guidelines. - Analytical verification of test atmosphere concentrations:
- yes
- Duration of exposure:
- 4 h
- Concentrations:
- 5 mg/L
- No. of animals per sex per dose:
- 5
- Control animals:
- no
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing:
- During exposure: 3 times
- After exposure:
Mortality: Twice daily
Clinical signs: On day 1, one and three hours after exposure and once daily thereafter until day 15
Body weights (individually): on day 1(pre-administration), 2, 4, 8 and 15.
- Necropsy of survivors performed: yes - Statistics:
- No statistical analysis was performed.
Results and discussion
Effect levels
- Key result
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- > 4.7 mg/L air (analytical)
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Mortality:
- No mortality occurred.
- Clinical signs:
- other: One male showed slow breathing during exposure. One male showed piloerection one hour after exposure. No further clinical signs were noted.
- Body weight:
- No abnormalities observed. Overall body weight gain in males and females was within the range expected for rats of this strain and age used in this type of study
- Gross pathology:
- No abnormalities were found at necropsy
- Other findings:
- - Actual exposure concentrations: The time-weighted mean actual concentration was 4.7 ± 0.13 mg/L. The nominal concentration (amount of test item used divided by the volume of pressurized air used) was 513 mg/L. The generation efficiency (ratio of actual and nominal concentration) was 0.9%.
- Particle size: The Mass Median Aerodynamic Diameter (MMAD) and geometric standard deviation (gsd) were determined twice during the exposure period.(see table 1)
Any other information on results incl. tables
Table 1 Aerodynamic particle size distribution in the test atmosphere
Measurement 1:
Stage |
Cut point (mm) |
Mass sampled (mg) |
Relative mass (%) |
Cumulative mass (% of total sampled) |
|
1 |
21.0 |
0.06 |
0.93 |
99.07 |
|
2 |
15.0 |
0.14 |
2.17 |
96.90 |
|
3 |
10.0 |
1.01 |
15.66 |
81.24 |
|
4 |
6.0 |
0.91 |
14.11 |
67.13 |
|
5 |
3.5 |
3.00 |
46.51 |
20.62 |
|
6 |
2.0 |
1.11 |
17.21 |
3.41 |
|
7 |
0.9 |
0.22 |
3.41 |
0.00 |
|
8 |
0.5 |
0.00 |
0.00 |
0.00 |
|
Back up |
0.25 |
0.00 |
0.00 |
0.00 |
|
MMAD1(μm): |
5.2 |
||||
gsd2: |
1.8 |
Measurement 2:
Stage |
Cut point (mm) |
Mass sampled (mg) |
Relative mass (%) |
Cumulative mass (% of total sampled) |
|
1 |
21.0 |
0.05 |
0.63 |
99.37 |
|
2 |
15.0 |
0.00 |
0.00 |
99.37 |
|
3 |
10.0 |
0.42 |
5.26 |
94.11 |
|
4 |
6.0 |
2.08 |
26.07 |
68.05 |
|
5 |
3.5 |
3.56 |
44.61 |
23.43 |
|
6 |
2.0 |
1.20 |
15.04 |
8.40 |
|
7 |
0.9 |
0.36 |
4.51 |
3.88 |
|
8 |
0.5 |
0.12 |
1.50 |
2.38 |
|
Back up |
0.25 |
0.19 |
2.38 |
0.00 |
|
MMAD1(μm): |
3.8 |
||||
gsd2: |
1.8 |
1 Mass Median Aerodynamic Diameter;2 Geometric standard deviation
Applicant's summary and conclusion
- Interpretation of results:
- GHS criteria not met
- Remarks:
- Not class
- Conclusions:
- In an acute inhalation study, performed according to OECD guideline 403 and GLP principles, the LC50 of URALAC P 1920C in rats was found to exceed 5 mg/L. Based on these results, the test item is not classified according to GHS and Regulation (EC) No. 1272/2008.
- Executive summary:
An acute inhalation study was performed according to OECD/EC guidelines and GLP principles. Five males and five females were exposed to an atmosphere with a time-weighted mean actual concentration of 4.7 ± 0.13 mg/L and observed for 14 days. No mortality occurred. One male showed slow breathing during exposure. One male showed piloerection one hour after exposure. No further clinical signs were noted, no unexpected effects on weight gain were observed and no abnormalities were seen at necropsy. These results show that the the LC50 of URALAC P 1920C in rats exceeds 5 mg/L.
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