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EC number: 203-505-6 | CAS number: 107-58-4
- 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
![](https://poisoncentres.echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_ecotoxicological-information.png)
Long-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- long-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study with acceptable restrictions
- Justification for type of information:
- Experimental test result performed using standard OECD test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 211 (Daphnia magna Reproduction Test)
- GLP compliance:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- - Pre-treatment of test chemical: The test chemical was prepared by dissolving 100 mg of test chemical in 100 mL of Adams media with 48 hours stirring to get the final concentration of 1000 mg/L. This stock solution will be filtered by using whatman filter paper no. 42, which will then analytically determine. The final solubility value obtained in media was used to prepare the remaining test concentrations from the above stock solution.
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
Test chemical was weighed and about 100mg in 100 ml of test chemical kept for stirring for 48 hours, which was then filtered and the concentration was anlytically determined.
- Controls: Test media M7 was directly used as the control.
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): no vehilce was used during study
- Concentration of vehicle in test medium (stock solution and final test solution(s) or suspension(s) including control(s)): no applicable - Test organisms (species):
- Daphnia magna
- Details on test organisms:
-
TEST ORGANISM
- Common name: Water flea
- Strain/clone: Straus
- Justification for species other than prescribed by test guideline: Test organism used was as per guidelines
- Age at study initiation (mean and range, SD): <24houes ols
- Length at study initiation (length definition, mean, range and SD): 0.35 cm
- Stage and instar at study initiation: neonate
- Method of breeding: daphnia were maintained in the Adams medium in similar conditions as per the test conditions, gravid females are seperated from the other daphinds for the collection of young neonates.
- Source: MicroBio tests Kleimoer 15B-9030 MARIAKERKE (GENT) BELGIUM
- Age of parental stock (mean and range, SD): 4-5 weeks
- Feeding during test: yes
- Food type: Fresh water algae (Selenestrum capricornutum)
- Amount: 0.1 mg C/Daphnia/day
- Frequency: thrice in a week
ACCLIMATION
- Acclimation period: Parent daphnids were acclimitised minimum for the period of 4 weeks in M7 medium before taking taking their neonates for study
- Acclimation conditions (same as test or not): same as test conditions
- Feeding frequency:
- Health during acclimation (any mortality observed): Parent daphnids were healthy.
QUARANTINE (wild caught): None
- Duration:
- Health/mortality:
- Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 21 d
- Hardness:
- > 140 mg/l as CaCO3
- Test temperature:
- 18.4 to 21.5°C
- pH:
- 7.1-8.4
- Dissolved oxygen:
- 6.7-7.1 mg/L
- Salinity:
- Not applicable
- Nominal and measured concentrations:
- 0 and 10 mg/l ( nominal concentration)
- Details on test conditions:
- TEST SYSTEM
- Test vessel: glass beaker
- Type (delete if not applicable): loosley covered to avoid the dust particles to fall into the media
- Material, size, headspace, fill volume: 50 mll beaker, 40 ml of test solutions, 10 ml head space
- Aeration: No aeration during study
- Type of flow-through (e.g. peristaltic or proportional diluter): Not applicable
- Renewal rate of test solution (frequency/flow rate): Thrice weekly
- No. of organisms per vessel: 1 organims/ vessels.
- No. of vessels per concentration (replicates): 10 vessels per concentrations
- No. of vessels per control (replicates): 10 vessels per control
- No. of vessels per vehicle control (replicates): Not applicable
- Test medium: M7 Media
OTHER TEST CONDITIONS
- Adjustment of pH: No adjustment
- Photoperiod: 16:8 light:dark conditions
- Light intensity: Not exceeding 1000-1500 lux
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : The evaluation of the NOEC was determined based on the number of offspring’s produced per living parent Daphnia.
TEST CONCENTRATIONS
- Spacing factor for test concentrations: Not appicable
- Justification for using less concentrations than requested by guideline: Not applicable
- Range finding study: Based on the available information on the short term daphniamagna concentrations for the long term studies are determined
- Test concentrations: 10 mg/L
- Results used to determine the conditions for the definitive study: 1/10 of the EC50 of Daphina immobilisation study was considerd for main study - Reference substance (positive control):
- not required
- Key result
- Duration:
- 21 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 10 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- reproduction
- Details on results:
- - Behavioural abnormalities:
no behavioural abnormalities were observed
- Observations on body length and weight: no significant difference was observed in the body length was observed in both parents and offsprings
- Mortality of control: no mortality was observed in control parents and offsprings
- Other adverse effects control: no adverse effects were observed
- Immobilisation of control: no immobilisation - Results with reference substance (positive control):
- Not applicable
- Reported statistics and error estimates:
- The statistical comparision was done by student T test method using Sys stat software
- Validity criteria fulfilled:
- yes
- Remarks:
- The mortality of the parent animal does not exceed 20% at the end of the test; The mean no. of living offspring produced per parent animal surviving at the end of the test is ≥60.
- Conclusions:
- Based on the effect on reproduction of the test daphnids, the 21 d NOEC value was determined to be 10 mg/l.
- Executive summary:
A chronic study was conducted for assesing the effect of test chemical. The study was performed in accordance with the principles of the OECD Guideline 211 (Daphnia magna Reproduction Test). Parent daphina were acclimitised in the similar conditions as maintined on the test. From this, gravid parents were isolated and miantined in the Adams medium offsprings were collected, and these nenonates were used in the study. The test organims was obatined from MicroBio tests Kleimoer 15B-9030 MARIAKERKE(GENT)BELGIUM. The Neonates whose age was less than <24 hours were selected. Test daphnids were fed with living cells of Selenestrum capricornutum and it was done thrice a week. The test chemical will be prepared by dissolving 100 mg of test chemical in 100 mL of Adams media with 48 hours stirring to get the final concentration of 1000 mg/L. This stock solution was filtered by using whatman filter paper no. 42, which was then analytically determined. The final solubility value obtained in media was used to prepare the remaining test concentrations from the above stock solution. The analytical determinations were performed by UV-VIS spectrophotometer. The pre-treated stock solution was then diluted with media in order to get the required test solutions. the linearity range selected for concentrations analysis and stock analysis was 0.3254, 0.6108, 6.8485, 1.1290, 1.4311, 1.6983 and 1.945 mg/L. The absorbance of resulting solution was measured using UV-VIS spectrophotometer against corresponding blank at lambda max (λmax). Standard curve was plotted against concentration verses absorbance and the maximum solubility was determined from the below standard curve. Analytical assessments were performed for selected test concentration at 1st, 2nd and 3rd week. The concentration of the test chemical being tested has been satisfactorily maintained within ± 20 % of the nominal concentration throughout the test. Therefore, the analysis of the results was based on nominal concentration. Test chemical conc. used in the defiinite study were 0 and 10 mg/l. Thus, limit test was performed at test chemical conc. of 10 mg/l. Test daphnids were exposed to test chemical conc. in a glass beaker for an exposure period of 21 days. Vessels were not aerated during the study. Adams medium was used as a test medium. Test conditions involve a temperature range of 18.4-21.5°C, 16:8 light:dark conditions and light intensity not exceeding 1000-1500 lux, respectively. Each test concentrations has 10 replicates and each replicate has 1 dapnids same number were taken for control goups. The evaluation of the NOEC was determined based on the number of offspring’s produced per living parent Daphnia. Defined concentrations of the test chemical led to a certain percentage reduction of the parthenogenetic reproduction rate at the end of the 21 day study period. The living offspring was counted daily along with the renewal of the test medium. However, test vessels were inspected daily for the occurrence of juveniles and marked accordingly. On the basis of the effect on reproduction of the test daphnids, the 21 d NOEC value was determined to be 10 mg/l. Thus, based on the NOEC value, test chemical was considered as non-toxic to aquatic invertebrates and hence, considered to be 'not classified' as per the CLP classification criteria.
Reference
Defined concentrations of the test chemical led to a certain percentage reduction of the parthenogenetic reproduction rate at the end of the 21 day study period. The living offspring was counted daily along w ith the renewal of the test medium. However, test vessels were inspected daily for the occurrence of juveniles and marked accordingly.
Table: Data for recording medium renewal, physical/chemical monitoring data, feeding, and daphnia reproduction, parent and offspring mortality
Nominal concentration: control
Day |
0 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
|
Medium renewal |
- |
- |
Y |
- |
- |
Y |
- |
Y |
- |
Y |
- |
- |
Y |
- |
Y |
- |
Y |
- |
- |
Y |
- |
- |
|
pH (new) |
8.4 |
- |
7.3 |
- |
- |
8.01 |
- |
7.1 |
- |
7.5 |
- |
- |
7.9 |
- |
7.7 |
- |
8.0 |
- |
- |
7.3 |
- |
7.9 |
|
O2 (mg/l) (new) |
8.5 |
- |
8.4 |
- |
- |
7.8 |
- |
8.0 |
- |
7.3 |
- |
- |
8.5 |
- |
8.0 |
- |
7.4 |
- |
- |
7.6 |
- |
7.4 |
|
Temp. (°C) (new) |
20.2 |
- |
19.5 |
- |
- |
20.1 |
- |
20.3 |
- |
18.8 |
- |
- |
20.0 |
- |
18.9 |
- |
21.5 |
- |
- |
19.0 |
- |
18.4 |
|
Food provided |
Y |
- |
Y |
- |
- |
Y |
- |
Y |
- |
Y |
- |
- |
Y |
- |
Y |
- |
Y |
- |
- |
Y |
- |
Y |
|
No. of live offspring per parent animal |
Total no. of live offspring/vessel |
||||||||||||||||||||||
V1 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
1 |
- |
- |
4 |
- |
- |
13 |
- |
- |
- |
8 |
2 |
28 |
V2 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
9 |
- |
- |
21 |
- |
- |
- |
32 |
- |
- |
62 |
V3 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
9 |
- |
- |
4 |
1 |
- |
31 |
1 |
- |
- |
38 |
- |
- |
66 |
V4 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
15 |
- |
- |
23 |
- |
- |
- |
38 |
- |
- |
- |
- |
76 |
V5 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
1 |
5 |
- |
8 |
- |
1 |
21 |
- |
- |
- |
42 |
- |
- |
78 |
V6 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
4 |
- |
11 |
- |
- |
- |
23 |
- |
- |
35 |
- |
- |
73 |
V7 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
3 |
- |
15 |
- |
- |
- |
19 |
- |
- |
41 |
- |
- |
78 |
V8 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
V9 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
10 |
- |
- |
15 |
- |
- |
17 |
- |
- |
- |
45 |
- |
- |
87 |
V10 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
7 |
- |
- |
17 |
- |
- |
21 |
- |
- |
- |
16 |
- |
81 |
Cumulative reproductivity |
= 609 |
No. of days |
|
0 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
1 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
2 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
3 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
4 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
5 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
6 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
7 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
8 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
9 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
10 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Nominal concentration: 10 mg/l
Day |
0 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
|
Medium renewal |
- |
- |
Y |
- |
- |
Y |
- |
Y |
- |
Y |
- |
- |
Y |
- |
Y |
- |
Y |
- |
- |
Y |
- |
- |
|
pH (new) |
8.3 |
- |
7.7 |
- |
- |
8.16 |
- |
7.6 |
- |
7.5 |
- |
- |
7.9 |
- |
8.1 |
- |
7.9 |
- |
- |
7.4 |
- |
7.8 |
|
O2 (mg/l) (new) |
8.4 |
- |
8.2 |
- |
- |
7.84 |
- |
7.8 |
- |
7.0 |
- |
- |
8.6 |
- |
7.8 |
- |
7.2 |
- |
- |
7.5 |
- |
7.2 |
|
Temp. (°C) (new) |
19.8 |
- |
19.5 |
- |
- |
20.1 |
- |
20.3 |
- |
18.9 |
- |
- |
20.0 |
- |
19.0 |
- |
21.3 |
- |
- |
19.1 |
- |
18.3 |
|
Food provided |
Y |
- |
Y |
- |
- |
Y |
- |
Y |
- |
Y |
- |
- |
Y |
- |
Y |
- |
Y |
- |
- |
Y |
- |
Y |
|
No. of live offspring per parent animal |
Total no. of live offspring/vessel |
||||||||||||||||||||||
V1 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
14 |
2 |
- |
27 |
- |
- |
- |
43 |
V2 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
11 |
- |
- |
40 |
51 |
V3 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
7 |
- |
17 |
- |
- |
- |
27 |
- |
51 |
V4 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
V5 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
V6 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
14 |
- |
- |
- |
50 |
64 |
V7 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
V8 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
V9 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
V10 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
12 |
1 |
- |
- |
45 |
- |
35 |
- |
Cumulative reproductivity |
= 302 |
No. of days |
|
0 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
16 |
17 |
18 |
19 |
20 |
21 |
1 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
2 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
3 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
4 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
5 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
M |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
6 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
7 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
M |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
8 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
M |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
9 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
M |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
|
10 |
Dead P |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Dead O |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
NOTE: ABBREVIATION'S USED FOR:
M: Mortality
#: First brood recognizable in brood pouch of parent daphnia
V: Vessels (V1...V10...V20 are replicates)
P: Parent
O: Offsprings
Description of key information
A chronic study was conducted for assesing the effect of test chemical. The study was performed in accordance with the principles of the OECD Guideline 211 (Daphnia magna Reproduction Test). Parent daphina were acclimitised in the similar conditions as maintined on the test. From this, gravid parents were isolated and miantined in the Adams medium offsprings were collected, and these nenonates were used in the study. The test organims was obatined from MicroBio tests Kleimoer 15B-9030 MARIAKERKE(GENT)BELGIUM. The Neonates whose age was less than <24 hours were selected. Test daphnids were fed with living cells of Selenestrum capricornutum and it was done thrice a week. The test chemical will be prepared by dissolving 100 mg of test chemical in 100 mL of Adams media with 48 hours stirring to get the final concentration of 1000 mg/L. This stock solution was filtered by using whatman filter paper no. 42, which was then analytically determined. The final solubility value obtained in media was used to prepare the remaining test concentrations from the above stock solution. The analytical determinations were performed by UV-VIS spectrophotometer. The pre-treated stock solution was then diluted with media in order to get the required test solutions. the linearity range selected for concentrations analysis and stock analysis was 0.3254, 0.6108, 6.8485, 1.1290, 1.4311, 1.6983 and 1.945 mg/L. The absorbance of resulting solution was measured using UV-VIS spectrophotometer against corresponding blank at lambda max (λmax). Standard curve was plotted against concentration verses absorbance and the maximum solubility was determined from the below standard curve. Analytical assessments were performed for selected test concentration at 1st, 2nd and 3rd week. The concentration of the test chemical being tested has been satisfactorily maintained within ± 20 % of the nominal concentration throughout the test. Therefore, the analysis of the results was based on nominal concentration. Test chemical conc. used in the defiinite study were 0 and 10 mg/l. Thus, limit test was performed at test chemical conc. of 10 mg/l. Test daphnids were exposed to test chemical conc. in a glass beaker for an exposure period of 21 days. Vessels were not aerated during the study. Adams medium was used as a test medium. Test conditions involve a temperature range of 18.4-21.5°C, 16:8 light:dark conditions and light intensity not exceeding 1000-1500 lux, respectively. Each test concentrations has 10 replicates and each replicate has 1 dapnids same number were taken for control goups. The evaluation of the NOEC was determined based on the number of offspring’s produced per living parent Daphnia. Defined concentrations of the test chemical led to a certain percentage reduction of the parthenogenetic reproduction rate at the end of the 21 day study period. The living offspring was counted daily along with the renewal of the test medium. However, test vessels were inspected daily for the occurrence of juveniles and marked accordingly. On the basis of the effect on reproduction of the test daphnids, the 21 d NOEC value was determined to be 10 mg/l. Thus, based on the NOEC value, test chemical was considered as non-toxic to aquatic invertebrates and hence, considered to be 'not classified' as per the CLP classification criteria.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 10 mg/L
Additional information
A chronic study was conducted for assesing the effect of test chemical. The study was performed in accordance with the principles of the OECD Guideline 211 (Daphnia magna Reproduction Test). Parent daphina were acclimitised in the similar conditions as maintined on the test. From this, gravid parents were isolated and miantined in the Adams medium offsprings were collected, and these nenonates were used in the study. The test organims was obatined from MicroBio tests Kleimoer 15B-9030 MARIAKERKE(GENT)BELGIUM. The Neonates whose age was less than <24 hours were selected. Test daphnids were fed with living cells of Selenestrum capricornutum and it was done thrice a week. The test chemical will be prepared by dissolving 100 mg of test chemical in 100 mL of Adams media with 48 hours stirring to get the final concentration of 1000 mg/L. This stock solution was filtered by using whatman filter paper no. 42, which was then analytically determined. The final solubility value obtained in media was used to prepare the remaining test concentrations from the above stock solution. The analytical determinations were performed by UV-VIS spectrophotometer. The pre-treated stock solution was then diluted with media in order to get the required test solutions. the linearity range selected for concentrations analysis and stock analysis was 0.3254, 0.6108, 6.8485, 1.1290, 1.4311, 1.6983 and 1.945 mg/L. The absorbance of resulting solution was measured using UV-VIS spectrophotometer against corresponding blank at lambda max (λmax). Standard curve was plotted against concentration verses absorbance and the maximum solubility was determined from the below standard curve. Analytical assessments were performed for selected test concentration at 1st, 2nd and 3rd week. The concentration of the test chemical being tested has been satisfactorily maintained within ± 20 % of the nominal concentration throughout the test. Therefore, the analysis of the results was based on nominal concentration. Test chemical conc. used in the defiinite study were 0 and 10 mg/l. Thus, limit test was performed at test chemical conc. of 10 mg/l. Test daphnids were exposed to test chemical conc. in a glass beaker for an exposure period of 21 days. Vessels were not aerated during the study. Adams medium was used as a test medium. Test conditions involve a temperature range of 18.4-21.5°C, 16:8 light:dark conditions and light intensity not exceeding 1000-1500 lux, respectively. Each test concentrations has 10 replicates and each replicate has 1 dapnids same number were taken for control goups. The evaluation of the NOEC was determined based on the number of offspring’s produced per living parent Daphnia. Defined concentrations of the test chemical led to a certain percentage reduction of the parthenogenetic reproduction rate at the end of the 21 day study period. The living offspring was counted daily along with the renewal of the test medium. However, test vessels were inspected daily for the occurrence of juveniles and marked accordingly. On the basis of the effect on reproduction of the test daphnids, the 21 d NOEC value was determined to be 10 mg/l. Thus, based on the NOEC value, test chemical was considered as non-toxic to aquatic invertebrates and hence, considered to be 'not classified' as per the CLP classification criteria.
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