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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Administrative data

Endpoint:
short-term toxicity to fish
Type of information:
experimental study
Adequacy of study:
disregarded due to major methodological deficiencies
Study period:
from 05-NOV-2001 to 09-NOV-2001
Reliability:
3 (not reliable)
Rationale for reliability incl. deficiencies:
other: see 'Remark'
Remarks:
Based on its vapour pressure, pent-3-enenitrile is a volatile compound. As a result, this property must be taken into account in the experimental design of ecotoxicological studies. In the current data, no sufficient details are provided to be sure this precaution has been taken. Thus the results presented are believed not to be reliable.

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2001
Report date:
2001

Materials and methods

Test guideline
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 203 (Fish, Acute Toxicity Test)
Principles of method if other than guideline:
There is no guideline indicated in the study report. Based on the few experimental details available, the method is closed to OECD Guideline 203. However, the level of information is too low to assess the potential deviations compared to this method.
GLP compliance:
no

Test material

Constituent 1
Chemical structure
Reference substance name:
Pent-3-enenitrile
EC Number:
225-060-7
EC Name:
Pent-3-enenitrile
Cas Number:
4635-87-4
Molecular formula:
C5H7N
IUPAC Name:
(3E)-pent-3-enenitrile

Sampling and analysis

Analytical monitoring:
not specified

Test solutions

Vehicle:
no
Details on test solutions:
PREPARATION AND APPLICATION OF TEST SOLUTION
No data

Test organisms

Test organisms (species):
Pimephales promelas
Details on test organisms:
No data

Study design

Test type:
static
Water media type:
freshwater
Limit test:
no
Total exposure duration:
96 h

Test conditions

Hardness:
No data
Test temperature:
21.6 °C
pH:
Test initiation: 7.5 - 7.6
Test completion: 7.5
Dissolved oxygen:
Test initiation: 8.7 mg/L
Test completion: 6 - 6.8 mg/L
Salinity:
Not applicable
Nominal and measured concentrations:
0.1, 1, 10 and 100 mg/L (nominal concentrations)
Details on test conditions:
TEST SYSTEM
- No. of organisms per vessel: 10
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
No further data

TEST MEDIUM / WATER PARAMETERS
- Intervals of water quality measurement: Dissolved oxygen and pH were measured at the test initiation and completion (i.e. after 0 and 96 hours).
No further data

OTHER TEST CONDITIONS
No data

EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
Mortality was assessed after 24, 48, 72 and 96 hours.

TEST CONCENTRATIONS
- Spacing factor for test concentrations: 10
No further data

Results and discussion

Effect concentrations
Duration:
96 h
Dose descriptor:
LC50
Effect conc.:
> 100 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
mortality (fish)

Applicant's summary and conclusion

Validity criteria fulfilled:
no
Conclusions:
As there is no indication on the potential care given to the volatility of the test substance, it is not possible to exclude the existence of abiotic phenomenon of degradation susceptible to lead to the disappearance of the test substance from the medium. Therefore, no conclusion can be drawn out regarding the toxicity of the test substance to fish.
Executive summary:

The acute toxicity of the test substance to fathead minnow (Pimephales promelas) was assessed in a 96h-hour static test. Groups of 10 fish were exposed to a control treatment or to 3PN concentrations of 0.1, 1, 10 and 100 mg/L. Mortality was observed after 24, 48, 72 and 96 housr of exposure. At the end of the test period, no mortality was observed, neither in the control treatment, nor in groups exposed to the different concentrations of 3PN. However, as there is no indication on the potential care given to the volatility of the test substance, it is not possible to exclude the existence of abiotic phenomenon of degradation susceptible to lead to the disappearance of the test substance from the medium. Therefore, no conclusion can be drawn out regarding the toxicity of the test substance to fish.