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EC number: 813-937-2 | CAS number: 111512-60-8
- 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
Repeated dose toxicity: inhalation
Administrative data
- Endpoint:
- short-term repeated dose toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 03/08/2015 - 08/01/2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 016
- Report date:
- 2016
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 412 (Subacute Inhalation Toxicity: 28-Day Study)
- Deviations:
- yes
- Remarks:
- See Principles of Method
- Principles of method if other than guideline:
- PROTOCOL DEVIATIONS
This study was conducted in accordance with the protocol and protocol amendments, except for the following.
• Protocol Section 7.2 states that controls will be set to maintain a temperature of 71 ± 5°F (approximately 22 ± 3°C) and a relative humidity of 50 ± 20% within the animal holding room and that temperature and relative humidity will be monitored continuously. From 13-Aug-2015 through 19-Aug-2015, WIL Research experienced a computer network issue that impacted the Metasys PMI System’s ability to automatically control and record environmental conditions for various areas of the facility. Impact Assessment: This deviation did not have a negative impact on the integrity or results of the study as sufficient environmental data were recorded automatically or manually to demonstrate that the animals were maintained under acceptable conditions.
• Protocol Section 8.1 states that animal will be acclimated to restraint in nose-only exposure restraint tubes by increasing the restraint time over the acclimation period (first day, 1 hour; second day, 2 hours; third day, 3 hours; fourth day, 4 hours; and fifth day, 6 hours). On the second day of acclimation, some males and females remained in the restraint tubes for 2 hours 19minutesto 2 hours 20 minutes. Impact Assessment: This deviation did not negatively impact the quality or integrity of the data or the outcome of the study because these times were only 1-2minutes outside the acceptable time range.
• Protocol Section 9.3.1 states that animals will receive a daily observation 0-1 hour (+0.25 hr) following the exposure. On study day 7, male no. 1959 in the 242,912 mg/m3 (40,000 ppm) group did not receive an observation following exposure. Impact Assessment: This deviation did not negatively impact the quality or integrity of the data or the outcome of the study because a single missed observation for a single animal had no effect or impact on the study results.
• Protocol Section 9.5states that food weights will be recorded weekly throughout the study period. On study day 13, all food jars were removed without being weighed. As a result, there is no food consumption data for the study day 7-14interval. Impact Assessment: This deviation did not negatively impact the quality or integrity of the data or the outcome of the study because there was no effect on body weight during the study day 7-14 interval, thus it is unlikely that there was an effect on food consumption during the same interval.
• Protocol Section 9.9.1 lists the tissues to be collected at necropsy, and Protocol Section 9.9.3 details the animals from which these tissues will be examined microscopically. The following tissues were missing, precluding microscopic examination: bronchial lymph nodes from 1 female in the control group and parathyroids (1 or both) from 4 males and 3 females in the control group and 2 males and 3 females in the 242,912 mg/m3 (40,000 ppm) group. Impact Assessment: This deviation did not negatively impact the quality or integrity of the data or the outcome of the study because the number of tissues examined from each treatment group was sufficient to allow detection of test substance-related alterations.
• Protocol Section 9.9.1 states that the nasal cavity and brain from all animals will be retained in 10% neutral-buffered formalin, and Protocol Section 9.9.3 details the animals from which these tissues will be examined microscopically. The nasal cavity and both olfactory bulbs from female no. 2007 in the control group were lost at necropsy and were not available for microscopic examination. Impact Assessment: This deviation did not negatively impact the quality or integrity of the data or the outcome of the study because the nasal cavity and olfactory bulbs from control group females were available.
• Protocol Section 9.9.1 states that the coagulating glands will be examined for all males at the time of necropsy. For the primary necropsy on 23-Sep-2015, the coagulating glands were selected for females only in the program that sets up the necropsy tissue list. Therefore, the gross examination of coagulating glands was not documented at the primary necropsy. Impact Assessment: This deviation did not negatively impact the quality or integrity of the data or the outcome of the study because the coagulating glands in the control and high-exposure groups were examined microscopically.
GLP DEVIATIONS
Subpart E 160.81(a) states that a testing facility shall have standard operating procedures in writing, setting forth study methods that management is satisfied are adequate to ensure the quality and integrity of the data generated in the course of the study. All deviations in a study from standard operating procedures shall be authorized by the study director and shall be documented in the raw data. Significant changes in established standard operating procedures shall be properly authorized in writing by management. During this study, the SOP for the use of the temperature and humidity calibration equipment was in the revision process. The proper form for use of an SOP in revisions was not used, and management and the Study Director did not authorize the new procedure prior to the revised SOP being issued.
Impact Assessment: This deviation had no impact on the study as the temperature and humidity calibration procedure used during the study was the same procedure that is described in the revised SOP that was approved by management.
Subpart G 160.130(e) states that all data entries shall be dated on the day of entry and signed or initialled by the person entering the data. The personnel embedding tissues in paraffin for female no. 1996 in the 60,728 mg/m3 (10,000 ppm) group and female nos.1995, 2000, 2018, and 2022 in the 151,820 mg/m3 (25,000 ppm) groups was not documented on 06-Oct-2015, the date the function was performed. The personnel boxing the microscopic slides was also not recorded on 03-Nov-2015 and therefore cannot be determined.
Impact Assessment: These inadvertent documentation errors were minor GLP deviations and had no impact on the study or the study results. - GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- (1Z)-1-chloro-2,3,3,3-tetrafluoroprop-1-ene
- EC Number:
- 813-937-2
- Cas Number:
- 111512-60-8
- Molecular formula:
- C3HClF4
- IUPAC Name:
- (1Z)-1-chloro-2,3,3,3-tetrafluoroprop-1-ene
- Test material form:
- gas
Constituent 1
- Specific details on test material used for the study:
- The purity of the test substance was 98.371%(lot no. 150407-1)and 98.493% (lot no. 150407-2). The test substance was stored at room temperature (approximately 18°C to 24°C) and was considered stable under this condition. A reserve sample from each shipment of the test substance was collected and stored in the WIL Research Archives.
Test animals
- Species:
- rat
- Strain:
- Crj: CD(SD)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- All animals were housed throughout acclimation and during the study i n an environmentally controlled room. The room temperature and relative humidity controls were set to maintain environmental conditions of 71±5°F (22±3°C) and 50±20%, respectively. Room temperature and relative humidity data were monitored continuously and were scheduled for automatic collection on an hourly basis. These data are summarized in Appendix F. Actual mean daily temperature ranged from 70.0°F to 71.4°F (21.1°C to 21.9°C) and mean daily relative humidity ranged from 42.3% to 55.9% during the study. Fluorescent lighting provided illumination for a 12-hour light (0600hours to 1800hours)/12-hour dark photoperiod. The light status (on or off) was recorded once every 1 5minutes. The 12-hour light/12-hour dark photoperiod was interrupted as necessary to allow for the performance of protocol-specified activities. Air handling units were set to provide a minimum of 10fresh air changes per hour.
Administration / exposure
- Route of administration:
- inhalation: gas
- Type of inhalation exposure:
- nose only
- Vehicle:
- air
- Details on inhalation exposure:
- The selected route of administration for this study was inhalation exposure because this is a potential route of unintended human exposure. Nose-only exposure methods were used to reduce overall test substance requirements. The 6-hour period of restraint was necessary to achieve the exposure duration set forth in the OECD 412 testing guideline.
- Analytical verification of doses or concentrations:
- yes
- Duration of treatment / exposure:
- 6 Hours
- Frequency of treatment:
- 5 days per week, over 4 weeks (minimum of 20 exposures)
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 ppm (nominal)
- Dose / conc.:
- 10 000 ppm (nominal)
- Dose / conc.:
- 25 000 ppm (nominal)
- Dose / conc.:
- 40 000 ppm (nominal)
- Dose / conc.:
- 60 728 mg/m³ air (nominal)
- Dose / conc.:
- 151 820 mg/m³ air (nominal)
- Dose / conc.:
- 242 912 mg/m³ air (nominal)
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent no treatment
Examinations
- Observations and examinations performed and frequency:
- Standard toxicity endpoints included clinical observations, body weights, food consumption, functional observational battery (FOB) and motor activity (MA) assessments, macroscopic examinations, organ weight determinations at necropsy, and microscopic examination of tissues. This pathology report addresses the anatomical pathology and clinical pathology endpoints of the study.
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- no effects observed
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- no effects observed
- Immunological findings:
- no effects observed
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Other effects:
- no effects observed
Effect levels
open allclose all
- Key result
- Dose descriptor:
- NOEC
- Effect level:
- > 244 946 mg/m³ air (analytical)
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Dose descriptor:
- NOEC
- Effect level:
- > 40 335 ppm (analytical)
- Based on:
- test mat.
- Sex:
- male/female
- Remarks on result:
- not determinable due to absence of adverse toxic effects
Target system / organ toxicity
- Key result
- Critical effects observed:
- no
Any other information on results incl. tables
All animals survived to the scheduled necropsies. There were no test substance-related clinical findings noted in males and females at any exposure level.
No test substance-related effects on body weights, body weight gains, or food consumption were observed in the 60,728 mg/m3 (10,000 ppm), 151,820 mg/m3 (25,000 ppm), or 242,912 mg/m3 (40,000 ppm) group males and females.
Functional observational battery parameters (home cage, handling, open field, sensory, neuromuscular, and physiological observations) and motor activity in males and females were not affected by test substance exposure at any exposure concentration.
Exposure to the test substance resulted in no test substance-related alterations in hematology, coagulation, serum chemistry, and urinalysis parameters, organ weights, or macroscopic or microscopic findings.
Applicant's summary and conclusion
- Conclusions:
- Based on the results of this study, exposure to HCFO-1224yd(Z) to Crl:CD(SD) rats at concentrations of 60,728 mg/m3 (10,000 ppm), 151,820 mg/m3 (25,000 ppm), and 242,912 mg/m3 (40,000 ppm) via nose-only inhalation for 6 hours per day on a 5-day per week basis for 28 days resulted in no lethality or test substance-related effects in males and females at any exposure level. Therefore, the no-observed-effect concentration (NOEC) was considered to be 242,912 mg/m3 (40,000ppm). The actual mean analyzed concentration at this exposure level was 244,946 mg/m3 (40,335 ppm).
- Executive summary:
Based on the results of this study, exposure to HCFO-1224yd(Z) to Crl:CD(SD) rats at concentrations of 60,728 mg/m3 (10,000 ppm), 151,820 mg/m3 (25,000 ppm), and 242,912 mg/m3 (40,000 ppm) via nose-only inhalation for 6 hours per day on a 5-day per week basis for 28 days resulted in no lethality or test substance-related effects in males and females at any exposure level. Therefore, the no-observed-effect concentration (NOEC) was considered to be 242,912 mg/m3 (40,000ppm). The actual mean analyzed concentration at this exposure level was 244,946 mg/m3 (40,335 ppm).
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