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EC number: 601-147-9 | CAS number: 111988-49-9
- 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://echa.europa.eu./o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_ecotoxicological-information.png)
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:
- 15 - 19 May 1995
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Version / remarks:
- 1992
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 0 (control), 6.48, 10.8, 18.0, 30.0 and 50 mg/L
- Sampling method: Water samples were taken from the center of the aquaria at test start and end.
- Sample storage conditions before analysis: - Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: Several volumes of a stock solution (5.00 g test substance and 50 ml dimethylformamide (DMF)) were diluted into the respective aquaria.
- Controls: control: dilution water only, solvent control: 500 µL DMF/L
- Chemical name of vehiclle: dimethylformamide
- Concentration of vehicle in test medium: stock solution: 100%, final test solutions: 64.75 - 500 µL/L, control: 0%, solvent control: 500µL/L
- Test concentration separation factor: 1.667 - Test organisms (species):
- Lepomis macrochirus
- Details on test organisms:
- TEST ORGANISM
- Common name: bluegill
- Lot: F3 / 95
- Source: obtained from Osage Catfisheries, Osage Beach, USA on 14 February 1995
- Length at study initiation: 3.1 + 0.3 cm (Mean + SD)
- Weight at study initiation: 0.7 + 0.2 g (Mean + SD)
ACCLIMATION
- Acclimation period: 14 days
- Acclimation conditions: same as test
- Type and amount of food during acclimation: Brutfutter FB50, Kronen Fischkraftfutter,
- Feeding frequency during acclimation: Fish were not fed 48 h before and during the study.
- Health during acclimation: less than 3% mortality
- Prophylactic treatment directly after arriving of the fish with Oxytetracyclin-Hydrochlorid (4 g/100 L water, 2*24h), beginning on February 14 and finishing on February 16, 1995 - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Hardness:
- 40 - 60 mg CaCo3/L
- Test temperature:
- 22.2 - 23.0 °C
- pH:
- 7.0 - 7.2
- Dissolved oxygen:
- 100 - 105 %
- Nominal and measured concentrations:
- Nominal concentrations: 0 (control), 0 (solvent control), 6.48, 10.8, 18.0, 30.0 and 50 mg/L
Mean measured concentrations: < LOQ (control), < LOQ (solvent control), 6.20, 10.6, 16.7, 28.4 and 48.7 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: aquaria
- Material, size, headspace, fill volume: glass, 32 x 36 x 38 cm ( l x d x h), 3.7 L, 40 L
- Aeration: no
- No. of organisms per vessel: 20
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
- No. of vessels per vehicle control (replicates): 1
- Biomass loading rate: 0.35 g/L
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Reconstituted water (Ca++: 0.384 mmole/L, Mg++: 0.096 mmole/L, Na+: 0.148 mmole/L, K+: 0.015 mmole/L, Cl-:0.783 mmole/L, HCO3-: 0.148 mmole/L, SO4-: 0.096 mmole/L)
- Culture medium different from test medium: no
- Intervals of water quality measurement: 0, 24, 48, 72 and 96 h after test start (dissolved oxygen, pH)
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16/8 h light/dark
- Light intensity: not reported
EFFECT PARAMETERS MEASURED: mortality and behavior (4, 24, 48, 72 and 96 h after test start)
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 1.667 - Reference substance (positive control):
- no
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 25.2 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 95% confidence interval = 16.7 - 48.7 mg test substance/L
- Details on results:
- - Mortality of control: 0%
- Reported statistics and error estimates:
- The LC50-values with 95%-confidence intervals for every 24-hour period if possible were calculated by using a computer program which estimated the LC50 using three statistical techniques: moving average, binomial probability or probit analysis.
- Sublethal observations / clinical signs:
Table 1: Analytical results
Nominal test concentration in mg test substance (mg pure a.s./L)
Measured concentrations
in mg pure a.s./L
Mean measured concentration in mg test substance/L
Percent of nominal
at day 0
at day 4
Mean
Control
< 0.05
< 0.05
-
-
-
Solvent control
< 0.05
< 0.05
-
-
-
6.48 (6.31)
6.15
5.93
6.04
6.20
96
10.8 (10.5)
10.4
10.3
10.4
10.6
99
18.0 (17.5)
16.4
16.0
16.2
16.7
93
30.0 (29.2)
27.5
27.7
27.6
28.4
95
50.0 (48.7)
46.9
47.9
47.4
48.7
97
Table 2: Summary of sublethal effects and mortality of thiacloprid to bluegill sunfish (L. macrochirus)
Mean measured concentrations in mg test substance/L
(mg pure a.s./L)
4h
24h
48h
72h
96h
Dead
Obs.
Dead
Obs.
Dead
Obs.
Dead
Obs.
Dead
Obs.
Control
0
-
0
-
0
-
0
-
0
-
Solvent control
0
-
0
-
0
-
0
-
0
-
6.20
0
-
0
DF
0
DF
0
DF
0
DF
10.6
0
DF
0
DF
0
DF, AP
0
DF, AP
0
DF, AP
16.7
0
DF, AP
0
DF, AP
0
DF, AP
0
DF, AP
0
DF, AP, V
28.4
0
DF, AP, OB,
AT, V
2
DF, AP, OB, AT, SR, V
4
DF, AP, OB, AT, SR, V
12
DF, AP, BO, V
14
DF, AP, BO
48.7
0
DF, AP, OB,
AT, V, TS
20
-
20
-
20
-
20
-
DF = Darkened coloration,
AP = quiescent – marked by a state of inactivity or abnormally low activity
OB = at water surface – rising and remaining unusually long at the surface
AT = labored respiration
V = vertical oriented – turned up or down in a vertical position and remaining in that position for an unusually long time
TS = loss of equilibrium-turned laterally, more or less, from the normal body orientation.
Table 1: Validity criteria for OECD 203 (2019)
Criterion from the guideline
Outcome
Validity criterion fulfilled
The mortality in the control(s) should not exceed 10% (or one fish if less than ten are used) at the end of the test
0%
yes
The dissolved oxygen concentration must have been at least 60 per cent of the air
saturation value throughout the test
100 - 105%
yes
There must be evidence that the concentration of the substance being tested has been
satisfactorily maintained, and preferably it should be at least 80% of the
nominal concentration throughout the test. If the deviation from the nominal
concentration is greater than 20 per cent, results should be based on the measured
concentration.
Mean measured concentrations range from 93 to 97% of nominal concentrations. Effect values refer to measured concentrations.
yes
- Validity criteria fulfilled:
- yes
- Remarks:
- For further, details, please refer to 'Any other information on results incl. tables'.
- Conclusions:
- The LC50 (96 h) for bluegill sunfish (Lepomis macrochirus) was determined to be 25.2 mg test substance/L (mean measured) under static conditions.
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 18 - 22 Aug 1997
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- other: FIFRA 72-3
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 0 (control), 0 (solvent control), 1.88, 3.75, 7.5, 15 and 30 mg a.i./L
- Sampling method: 10 mL samples were collected from the aquaria at mid-depth using a glass pipet on day 0 and 4.
- Sample storage conditions before analysis: Test solution samples were analyzed on the same day as collection. - Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: A primary stock solution was prepared by dissolving 30.6123 g of test substance into 250 mL of dimethylformamide (DMF). A secondary stock solution was prepared by dissolving 12.5 mL (1.5 g a.i./L) of the primary stock solution into a total volume of 25 mL DMF (60 mg/mL). This stock solution was used to prepare the batches of different test solution.
- Differential loading: no
- Controls: control: dilution water only, solvent control: dilution water and 500 µL DMF/L
- Chemical name of vehicle: dimethylformamide (DMF)
- Concentration of vehicle in test medium: stock solution: 100%, final test solutions: 250 - 469 µL/L, control: 0%, solvent control: 500 µL/L
- Test concentration separation factor: 2 - Test organisms (species):
- Cyprinodon variegatus
- Details on test organisms:
- TEST ORGANISM
- Common name: sheepshead minnow
- Lot no: ABS080197
- Source: from Aquatic Biosystems, Fort Collins, USA (on 01 Aug 1997)
- Age at study initiation: approx. 75 days
- Length at study end: 15 - 24 mm (20.3 ± 2.2 mm)
- Weight at study initiation: 0.1 - 0.4 g ww (0.23 ± 0.07 g)
ACCLIMATION
- Acclimation period: 17 days
- Acclimation conditions: same as test (exception: temperature was between 23 and 31 °C for four days (12-9 days prior test start, fish did not exhibit any abnormal behavior or mortality as a result of this change in temperature)
- Type and amount of food during acclimation: newly hatched brine shrimp and/or a commercial fish food (Tetramin® or trout chow)
- Feeding frequency during acclimation: daily (no feeding 48 hours prior test)
- Health during acclimation: no - Test type:
- static
- Water media type:
- saltwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Test temperature:
- 21.6 - 23.1 °C
- pH:
- 7.2 - 7.8
- Dissolved oxygen:
- 5.2 - 6.0 mg/L (66 - 76 %)
- Salinity:
- 17 ‰
- Nominal and measured concentrations:
- Nominal concentrations: 0 (control), 0 (solvent control), 1.88, 3.75, 7.5, 15 and 30 mg a.i./L
Mean measured concentrations: < LOQ (control), < LOQ (solvent control), 1.89, 3.50, 7.55, 15.5 and 30.7 mg a.i./L - Details on test conditions:
- TEST SYSTEM
- Test vessel: aquaria
- Material, size, headspace, fill volume: stainless steel, 32.4 x 24 x 26.5 cm (l x wx h), 3.6 L, 17 L
- Aeration: no
- No. of organisms per vessel: 20 (in 7.5 mg/L: 21)
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
- No. of vessels per vehicle control (replicates): 1
- Biomass loading rate: 0.27 g/L
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Reverse osmosis (RO) water: Treated city water that been dechlorinated with sodium metabisulfite, passed through a multimedia filter and granular activated carbon units, passed through a 1 micron filter, and demineralized by conventional softeners, and treated by double pass reverse osmosis and finally sterilized by ultraviolet light.
- Chlorine: < 0.003 mg/L
- Alkalinity: 33 mg/L (as CaCO3)
- Culture medium different from test medium:
- Intervals of water quality measurement: dissolved oxygen, salinity and pH after 0, 48, 96 hours
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16:8 h / light:dark
- Light intensity: 820 lux
EFFECT PARAMETERS MEASURED: mortality and behavioral observations (after 24, 48, 72 and 96 hours)
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Range finding study
- Test concentrations: 0.1 - 100 mg/L
- Results used to determine the conditions for the definitive study: Mortality and sublethal effects were observed at 10 mg/L and higher concentrations. No mortality or sublethal effects were noted at nominal concentrations below 10 mg/L. - Reference substance (positive control):
- no
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 19.7 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 95% confidence interval = 15.5 - 30.7 mg a.i./L
- Details on results:
- - Other biological observations:
15% mortality at the 15.5 mg a.i./L test level and 100% mortality at the 30.7 mg a.i./L test level
- Mortality of control: 0%
- Effect concentrations exceeding solubility of substance in test medium: No undissolved test substance was observed in the test chambers. - Reported statistics and error estimates:
- The 96-hour LC50 value and the 95 percent confidence limits were calculated by a LC50 computer program developed by Stephan et al. (1982) using the following statistical methods: binomial probability, moving average angle, and probit.
- Sublethal observations / clinical signs:
Table 1: Cumulative mortality and behavioural observations of the sheepshead minnow exposed to thiacloprid
Mean measured concentration
[mg/L]
24 h
48 h
72 h
96 h
Dead
Observations
Dead
Observations
Dead
Observations
Dead
Observations
Control
0
20 N
0
20 N
0
20 N
0
20 N
Solvent control
0
20 N
0
20 N
0
20 N
0
20 N
1.89
0
20 N
0
20 N
0
20 N
0
20 N
3.50
0
20 N
0
20 N
0
20 N
0
20 N
7.55
0
21 Q
0
21 Q
0
16 Q; 5 N
0
19 Q; 2 N
15.5
2
18 Q
3
17 Q
3
14 Q; 3 N
3
15 Q; 2 N
30.7
20
-
20
-
20
-
20
-
Key to Observations: N = Normal; Q = Quiescent
Table 2: Measured concentrations during the 96-hour exposure test
Sampling
Measured test concentrations
Nominal concentration
[mg/L]
Day 0
[mg/L]
Day 4
[mg/L]
Mean
[mg/L]
Percent of nominal
Control
< 0.2
< 0.2
--
-
Solvent control
< 0.2
< 0.2
-
-
1.88
1.85
1.93
1.89
101
3.75
3.44
3.56
3.50
93
7.5
7.46
7.6
7.55
101
15
15.2
15.8
15.5
103
30
30.7
a
30.7
102
aAll fish at 30 mg/L were dead prior to day 4, therefore no analysis was needed.
Table 1: Validity criteria for OECD 203 (2019)
Criterion from the guideline
Outcome
Validity criterion fulfilled
The mortality in the control(s) should not exceed 10% (or one fish if less than ten are used) at the end of the test
0%
yes
The dissolved oxygen concentration must have been at least 60 per cent of the air
saturation value throughout the test
66 - 76%
yes
There must be evidence that the concentration of the substance being tested has been
satisfactorily maintained, and preferably it should be at least 80% of the
nominal concentration throughout the test. If the deviation from the nominal
concentration is greater than 20 per cent, results should be based on the measured
concentration.
93 - 103%
yes
- Validity criteria fulfilled:
- yes
- Remarks:
- For further, details, please refer to 'Any other information on results incl. tables'.
- Conclusions:
- The LC50 (96 h) for sheepshead minnow (Cyprinodon variegatus) was determined to be 19.7 mg a.i./L (mean measured) under static conditions.
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 20 - 24 Feb 1995
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Version / remarks:
- 1992
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 0 (control), 0 (solvent control), 5.18, 8.64, 14.4, 24.0 and 40.0 mg/L
- Sampling method: samples were taken from the center of the aquaria at the beginning and end of the test - Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: A primary stock solution was prepared by dissolving 4.04 g of test substance into 50 L of dimethylformamide (DMF). This stock solution was used to prepare the batches of different test solution.
- Differential loading: no
- Controls: control: dilution water only, solvent control: dilution water and 500 µL DMF/L
- Chemical name of vehicle: dimethylformamide (DMF)
- Concentration of vehicle in test medium: stock solution: 100 %, final test solutions: 65 - 500 µL/L, control: 0 %, solvent control: 500 µL/L
- Test concentration separation factor: 1.667 - Test organisms (species):
- Oncorhynchus mykiss (previous name: Salmo gairdneri)
- Details on test organisms:
- TEST ORGANISM
- Common name: rainbow trout
- Lot no.: F7 / 94
- Source: Dr. Rosengarten, Oesede-Georgsmarienhutte, Germany (obtained as as green eggs and milt at 13 Oct 1994)
- Length at study initiation: 4.4 + 0.3 cm (mean + SD)
- Weight at study initiation: 1.2 + 0.3 g (mean + SD)
- Holding conditions: held in culture tanks on a 16/8 hour light/dark photoperiod according to Braun et al., commercial trout diet (Brutfutter FB50, Kronen Fischkraftfutter)
ACCLIMATION
- Acclimation period: 48 h
- Acclimation conditions: same as test
- Health during acclimation: < 3 % mortality - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Hardness:
- 40 - 60 mg CaCO3/L
- Test temperature:
- 10.3 - 10.8 °C
- pH:
- 7.0 - 7.4
- Dissolved oxygen:
- 98 - 99%
- Nominal and measured concentrations:
- Nominal concentrations: 0 (control), 0 (solvent control), 5.18, 8.64, 14.4, 24.0 and 40.0 mg/L
Mean measured concentration: < LOD, < LOD, 4.99, 8.16, 13.3, 22.0 and 37.5 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: aquaria
- Material, size, headspace, fill volume: glass, 32 x 36 x 38 cm ( l x d x h), 3.7 L, 40 L
- Aeration: no
- No. of organisms per vessel: 20
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 1
- No. of vessels per vehicle control (replicates): 1
- Biomass loading rate: 0.6 g/L
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Reconstituted water by adding salt stock solutions to demineralized water (Ca++: 0.384 mmole/L, Mg++: 0.096 mmole/L, Na+: 0.148 mmole/L, K+: 0.015 mmole/L, Cl-:0.783 mmole/L, HCO3-: 0.148 mmole/L, SO4-: 0.096 mmole/L)
- Culture medium different from test medium: no
- Intervals of water quality measurement: 0, 24, 48, 72 and 96 h after test start (dissolved oxygen, pH)
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16/8 h light/dark
- Light intensity: not reported
EFFECT PARAMETERS MEASURED: mortality and behavior (4, 24, 48, 72 and 96 h after test start)
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 1.667 - Reference substance (positive control):
- no
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 30.5 mg/L
- Nominal / measured:
- meas. (arithm. mean)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Remarks on result:
- other: 95% confidence interval: 27.0 - 34.1 mg test substance/L
- Details on results:
- - Mortality of control: 0 %
- Validity criteria fulfilled:
- yes
- Conclusions:
- The LC50 (96 h) for rainbow trout (Oncorhynchus mykiss) was determined to be 30.5 mg test substance/L (mean measured) under static conditions.
Referenceopen allclose all
Description of key information
LC50 (96 h) = 25.2 mg/L (mean measured, OECD 203, Lepomis macrochirus)
LC50 (96 h) = 19.7 mg/L (mean measured, FIFRA Guideline 72-3, Cyprinodon variegatus)
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Dose descriptor:
- LC50
- Effect concentration:
- 25.2 mg/L
Marine water fish
Marine water fish
- Dose descriptor:
- LC50
- Effect concentration:
- 19.7 mg/L
Additional information
Three experimental GLP studies are available testing the acute toxicity of 3-(2-chlor-5-pyridyl-methyl)-cyanimino-1,3-thiazolidin towards fish. Two studies were performed with freshwater fish Lepomis macrochirus and Oncorhynchus mykiss. One study tested the effects of the test substance on marine sheepshead minnow Cyprinodon variegatus.
In the key freshwater study, bluegill (L. macrochirus) were exposed for 96 hours under static conditions to five concentrations of the test item ranging from 6.20 to 48.7 mg/L (mean measured) as well as a solvent control (500 µL dimethylformamide (DMF)/L and a (water) control according to OECD 203. Mean measured test concentrations (analysed at the start and end of the exposure period) ranged from approximately 93 % - 99 % of nominal concentrations. The results of the study were based on mean measured concentrations. The LC50 (96 h) value was determined to be 25.2 mg/L, with a 95 % confidence interval of 16.7 to 48.7 mg/L.
A further freshwater study performed with the rainbow trout (O. mykiss) was determined in a static 96-hour test. In this test, five groups of fish were exposed to nominal concentrations between 5.18 and 40 mg/L. An additional group of fish was exposed to the highest used solvent concentration (500 µl DMF/L test water). A further control group of fish was exposed to untreated test water. Mean measured test concentrations of the test substance during the whole test period ranged from 93 - 96 % of nominal concentrations.
The marine key study sheepshead minnow (C. variegatus) was conducted according to EPA FIFRA 72-3. Fish were exposed to the test item nominal concentrations ranging from 1.88 to 30.0 mg/L. The mean measured concentrations during the test period ranged from 93 - 103 % of the nominal concentrations. The LC50 (96 h) was determined to be 19.7 mg a.i./L (mean measured). The LC50 (96 h) was determined to be 30.5 mg test substance/L (expressed as mean measured concentration).
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.
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