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EC number: 807-040-5 | CAS number: 4538-42-5
- 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 fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2017
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Remarks:
- Monitoring analysis was performed using TOC. No substance specific method was used.
- Qualifier:
- according to guideline
- Guideline:
- other: (HJ/T 153-2004), "The Guidelines for the Testing of Chemicals, Effects on Biotoc Systems" (the 2nd edition) (2013)
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Deviations:
- yes
- Remarks:
- The fish species in the test in not one of the recommended species in the OECD guideline 203
- Principles of method if other than guideline:
- Preparation of the test solutions method deviated from protocol. According to protocol, W AFs
(Water accommodated fractions) method will be adopted in the limit test, however, it was found
that the test solution clarified and transparent with the test substance stirring 30 min in water.
According to the information provided by sponsor, the test substance is insoluble and hydrolyzed
in water quickly, and the hydrolyzate is soluble in water. Thus, test solutions were prepared by
directly dissolving appropriate amount of test substance in dilution medium and then facilitating
its dispersion by stirring for 30 min in the limit test. The deviation did not affect the accuracy and
scientificity for the test results. - GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- During the main test at 0, 24, 48, 72 and 96 h
- Vehicle:
- no
- Details on test solutions:
- Preparation of the Test Solutions
In the test, test solutions were prepared by directly dissolving appropriate amount of test
substance in dilution medium and then facilitating its dispersion by stirring for 30 min. The test
solution was clear and transparent. In the limit test, a volume of 9L test solutions obtained was
the evenly distributed to 3 test tanks. - Test organisms (species):
- other: Gobiocypris rarus (rare minnow)
- Details on test organisms:
- The Rare minnow, Gobiocypris rarus, was used in the test on the basis of such important
practical criteria as, for example, their ready availability throughout the year, ease of maintenance,
convenience for testing and any relevant economic, biological or ecological factors. The test
species of Rare minnow, Gobiocypris rarus (Batch No.: F201701I 5G), were bred by our own lab.
A population of a single stock was used in the test.
(1) Holding offish
Fish to be used in the test were held for at least 7 days in water of the quality and temperature to
be used in the test.
A photoperiod of 12 hours light, provided by overhead fluorescent tubes, and 12 hours dark was
maintained. The oxygen concentration was varied from 86 % to 93 % of the air saturation. And
the temperature was controlled between 22.8°C and 23.2°C, pH: 7.65-7.74.
The fish was fed daily during the holding period on proprietary fish food. They were held without
food for approximately 24 hours before being placed into the test vessels. The ingredients of the
fish food are given as follows:
Crude Protein> 30.0%
Crude Fat> 2.0%
Crude Fibre< 3.0%
Crude Ash< 12.0%
Moisture < I 0.0%
Characteristics of the fish food are measured at least twice a year by Jiangsu Provincial Center for
Disease Prevention and Control. The latest measuring result is showed in Table 11.
(2) Criteria of fish selection
During the holding period the tanks was inspected daily and any debris or unhealthy or dead fish
removed.
After the 48 hour settling-in period, no mortality was observed in the following 7 days. So the
batch of fish (Batch No.: F201701I5G) was accepted.
The average wet-weight and length of the fish used in the definitive test was 0.223 g and 2.44 cm,
with relative standard deviation (RSD) of 4.71% and 4.47%, respectively - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 96 h
- Hardness:
- 145 mg(CaC03)/L
- Test temperature:
- 23°C
- pH:
- between 7.79 and 7.89
- Dissolved oxygen:
- 77-95% of air saturation
- Nominal and measured concentrations:
- Measured concentrations according to TOC
- Details on test conditions:
- TEST SYSTEM
- Renewal rate of test solution (frequency/flow rate): each 24 hours
- No. of organisms per vessel: 7
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 3
OTHER TEST CONDITIONS
- Photoperiod: 12 hours photoperiod daily
- At 24, 48, 72 and 96 h, the mortalities of the fish were recorded, and observations on individual
behaviour were performed. Meanwhile, measurements of pH, dissolved oxygen and temperature
were can-ied out and recorded dai ly.
- Reference substance (positive control):
- yes
- Remarks:
- Potassium dichromate, K2Cr20 7, CAS: 7778-50-9; Purity: ::'.:': 99.8%; Lot number: L VC0052; Beijing Leon Technology Co. Ltd.
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 100 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- element (dissolved fraction)
- Basis for effect:
- mortality (fish)
- Sublethal observations / clinical signs:
Mortality during main test:
Nominal conc. (mg/L Measured conc. (mg/L Initial # of fish Number of dead fish blank control nd 7 24h 0 48h
0
72h
0
96h
0
blank control nd 7 0 0 0 0 blank control nd 7 0 0 0 0 100 93.9 7 24h 0 48h
0
72h
0
96h
0
100 93.9 7 0 0 0 0 100 93.9 7 0 0 0 0 - Validity criteria fulfilled:
- yes
- Remarks:
- 1 Control group was placed into test water alone. 2 Reference substance test K2Cr20 7 resulting 24 h-LC50 of 282 mg/L. 3 pH values of the test media were between 7.79 and 7.89, the Dissolved Oxygenvaried from 77 % to 95 % of the air saturation
- Conclusions:
- The results showed that under valid semi-static conditions (24 h renewal), the 96 h-LC50 of test
substance to fish (Rare minnow, Gobiocypris rarus) was greater than the nominal concentration
of 100 mg/L (mean measured concentration 93.9 mg/L), while the maximum concentration
causing no mortality (96 h-LC0) was equal to the nominal concentration of 100 mg/L (mean
measured concentration 93.9 mg/L). i.e.:
96 h-LCso > 100 mg/L (mean measured concentration 93 .9 mg/L);
96 h-LCo = 100 mg/L (mean measured concentration 93.9 mg/L). - Executive summary:
Under semi-static conditions (24 h renewal), the acute toxicity of the test substance of POI to
Rare minnow (Gobiocypris rarus) was conducted according to: "The guidelines for the testing of
chemicals" (HJ/T 153-2004), "The Guidelines for the Testing of Chemicals, Effects on Biotoc
Systems" (the 2nd edition) (2013); and with reference to Procedure 203 of the "Guidelines for
Testing of Chemicals" of the OECD: "Fish, Acute Toxicity Test" ( 1992).
According to the information provided by sponsor, the test substance is insoluble and hydrolyzed
in water quickly. Since there is no standard of hydrolyzate, UPLC or GC cannot be used to
determine the hydrolyzate's concentration in water accurately. While TOC method can accurately
detect the concentration of the test substance in test water, and characterize the stability of the test
substance.
A range-finding test with several concentrations was performed (1.0, 10.0 and 100 mg/L nominal).
Semi-static conditions (24 h renewal) method was adopted in limit test. Based on the results of
the range-finding test, the concentration of 100 mg/L was assigned in limit test. For each test tank
3 L test solution was filled in. 3 replicate was assigned for each treatment group and control
group, while the initial number of testing fish was 7 for each group.
The test fish were randomly chosen and put in appropriate test solutions after the temperature has
been adjusted to the required value. This was done in 30 min.
During the test period, the pH values of the control mediums and test mediums were between
7.79 and 7.89, the Dissolved Oxygen (DO) values varied from 77 % to 95 % of the air saturation
at the test temperature; the total hardness was in the range of 155 mg (CaC03)/L to 162 mg
(CaC03)/L; the temperature of the test mediums was maintained in the range of 23.0 °C to 23.2
°C and all fishes in the control group were normal. With the same conditions, K2Cr20 7 was used
as the positive control substance, and the resulting 24 h-LCso was 282 mg/L.
During the test period, all fish in the control groups and treated groups were alive and appeared
normal. The results showed that under valid semi-static conditions (24 h renewal), the 96 h-LC50
of test substance to fish (Rare minnow, Gobiocypris rarus) was greater than the nominal
concentration of 100 mg/L (mean measured concentration 93 .9 mg/L), while the maximum
concentration causing no mortality (96 h-LC0) was equal to the nominal concentration of I 00
mg/L (mean measured concentration 93.9 mg/L). i.e.:
96 h-LC50 > 100 mg/L (mean measured concentration 93.9 mg/L);
96 h-LC0 = 100 mg/L (mean measured concentration 93.9 mg/L).
Reference
Description of key information
The results showed that under valid semi-static conditions (24 h renewal), the 96 h-LC50 of test substance to fish (Rare minnow, Gobiocypris rarus) was greater than the nominal concentration of 100 mg/L (mean measured concentration 93.9 mg/L), while the maximum concentration
causing no mortality (96 h-LC0) was equal to the nominal concentration of 100 mg/L (mean measured concentration 93.9 mg/L). i.e.:
96 h-LCso > 100 mg/L (mean measured concentration 93 .9 mg/L);
96 h-LCo = 100 mg/L (mean measured concentration 93.9 mg/L). (Wu 2017)
The 96h-LC0 for 1,6 -diisocyanatohexane (CAS 822-06-0) which is a similar substance as Pentane, 1,5 - diisocyanato was
found to be > 82.8 mg/L (Caspers, 2000)
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Dose descriptor:
- LC50
- Effect concentration:
- 100 mg/L
Additional information
"Should read: > 100 mg/L"
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