Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 233-195-8 | CAS number: 10061-01-5
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 29th November 1988 - 17th July 1989
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study conducted in accordance with generally accepted scientific principles, possibly with incomplete reporting or methodological deficiencies, which do not affect the quality of the relevant results.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 989
- Report date:
- 1989
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Deviations:
- not specified
- Qualifier:
- according to guideline
- Guideline:
- EPA OTS 797.1300 (Aquatic Invertebrate Acute Toxicity Test, Freshwater Daphnids)
- Deviations:
- not specified
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- (Z)-1,3-dichloropropene
- EC Number:
- 233-195-8
- EC Name:
- (Z)-1,3-dichloropropene
- Cas Number:
- 10061-01-5
- Molecular formula:
- C3H4Cl2
- IUPAC Name:
- 1,3-dichloroprop-1-ene
- Details on test material:
- The sample of cis-1,3-dichloropropene was obtained from Shell Nederland Raffinaderij B.V., Rotterdam, (batch number 1986; 88009).
Calculated mean purity of 96% m/m
Constituent 1
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: all
- Sampling method: Media samples were taken from the D. magna test system at the start (0 hour) and at the end (48 hours) of the toxicity test. No D. maina were present in the samples taken for analysis.
- Sample storage conditions before analysis: ambient temperature, approximately 20 ºC
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
Quantities of a stock solution of cis-1,3-dichloropropene in reconstituted fresh water were added to quadruplicate sets of 150 ml conical flasks containing reconstituted fresh water to give, when completely full, an approximately logarithmic series of nominal concentrations ranging from 0.58 - 36 mg/l.
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: freshwater water flea
- Strain: Daphnia magna (strauss)
- Source: a laboratory culture. The culture is derived from a strain obtained (via ICI Brixham Laboratory) from I.R.Ch.A., France
- Age at study initiation (mean and range, SD): less that 24 hours
- Weight at study initiation (mean and range, SD): NDA
- Length at study initiation (length definition, mean, range and SD):NDA
- Valve height at study initiation, for shell deposition study (mean and range, SD): NDA
- Peripheral shell growth removed prior to test initiation: NDA
- Method of breeding: The D. magna are cultured in 1 litre pyrex glass beakers containing 0.8 litre reconstituted fresh water. Each vessel and its contents are referred to as a 'culture'. New cultures are started with animals less than 24 h old, at a density of about 12 per litre.
- Feeding during test: NDA
ACCLIMATION
- Acclimation period: Young for use in acute toxicity tests are collected from cultures aged between 15 and 28 days.
- Acclimation conditions (same as test or not): yes
- Type and amount of food: Chlorella vulgaris to give a concentration of approximately 0.15 x 10^6 cells/ml
- Feeding frequency: daily
- Health during acclimation (any mortality observed): NDA
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Post exposure observation period:
- N/A
Test conditions
- Hardness:
- 176 mg/l CaCO3
- Test temperature:
- 18 - 22 ºC
- pH:
- 7.6 - 8.4
- Dissolved oxygen:
- 8.8 - 9.8 mg/l
- Salinity:
- NDA
- Nominal and measured concentrations:
- Nominal: 0.58, 1.05, 1.9, 3.4, 6.1, 11, 20, 36 mg/L
Mean Measured: 0.32, 0.55, 1.1, 1.4, 2.9, 5.0, 9.4, 16.4 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: 150 ml connical flasks
- Type (delete if not applicable): closed
- Material, size, headspace, fill volume: 150 ml
- Aeration: no
- Type of flow-through (e.g. peristaltic or proportional diluter): N/A
- Renewal rate of test solution (frequency/flow rate): No
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 5
- No. of vessels per control (replicates): 5
- No. of vessels per vehicle control (replicates): N/A
- Biomass loading rate: NDA
TEST MEDIUM / WATER PARAMETERS
The water used for the culturing and testing of D. magna was a reconstituted fresh water prepared by dissolving the following amounts of Analar grade salts in glass-distilled deionised water:-
NaHCO3
CaSO4·2H2O
MgSO4
KCl
192 mg/l
120 mg/l
120 mg/l
8 mg/l
This recipe has been recommended as one suitable for producing a 'hard' water by the U.S. Environmental Protection Agency (1975). Before use for culturing, a soil extract is added to the reconstituted fresh water at a rate of 20 ml/l. The soil extract is prepared by autoclaving 100 g soil per litre of distilled water for 15 minutes at 120°C. Solids are removed by filtration through Whatman GF/C paper.
OTHER TEST CONDITIONS
- Adjustment of pH: Not mentioned
- Photoperiod: 16 hours light, 8 hours dark.
- Light intensity: NDA
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : Mobility
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 1.8
- Justification for using less concentrations than requested by guideline: N/A
- Range finding study: NDA - Reference substance (positive control):
- no
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 1.4 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: 95 % CL (1.3 - 1.7)
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 1.1 mg/L
- Nominal / measured:
- meas. (geom. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- The highest mean measured concentration of cis-1,3,-dichloropropene causing no immobilization within the period of the test was 1.1 mg/l. The lowest concentration causing 100, immobilization within the period of the test was 2.9 mg/l.
The 6, 12 24 and 48 h EC50 values were calculated to be 11; 3.3; 2.6 and 1.4 mg/l respectively (95 % confidence/fiducial* limits 9.8 - 12, 3.0 - 3.6, 2.2 - 3.1* and 1.3 - 1.7 mg/l).
Since cis-l,3-dichloropropene was observed to be stable in a mixture of 1 + 3 v/v water + acetone for at least 10 days, it is unlikely to have decomposed to any significant extent in the aqueous test media during the tests. Losses from the test system by volatilization should have been small, since all tests were conducted in sealed test vessels with no head space. The most likely explanation for the low initial concentrations relative to the nominal values is therefore adsorption onto container surfaces during preparation and testing of media. - Results with reference substance (positive control):
- N/A
- Reported statistics and error estimates:
- All calculations were based upon the mean measured concentration of cis-l,3-dichloropropene in the test solutions over the relevent exposure period.
The 6, 12 and 48 h EC50 values (those concentrations calculated to cause a 50 % immobilization after 6, 12 and 48 h exposure) were calculated using the moving average-angle method (US Environmental Protection Agency, 1985). The 24 h EC50 value was calculated using probit analysis (Finney, 1971). All calculations were performed after log transformation of the concentrations.
Any other information on results incl. tables
See the mortality data in the below attached table.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The 48 hour EC50 to Daphnia manga of (Z)-1,3-dichloropropene was determined as 1.4 mg/L as a mean measured concentration. 48 hour NOEC = 1.1 mg/L.
- Executive summary:
Juvenile Daphnia magna were exposed under static conditions to (Z)-1,3-dichloropropene for 48 hours at mean measured concentrations of 0.32, 0.55, 1.1, 1.4, 2.9, 5.0, 9.4, 16.4 mg/L, in accordance with EU method C.2. and conducted to GLP standard.
The 48 hour EC50 to Daphnia magna of (Z)-1,3-dichloropropene was determined as 1.4 mg/L as a mean measured concentration. 48 hour NOEC = 1.1 mg/L.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.