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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

Ecotoxicological information

Toxicity to aquatic algae and cyanobacteria

Administrative data

Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
experimental study
Adequacy of study:
key study
Study period:
Study completion date 15 May 2017
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2017
Report date:
2017

Materials and methods

Test guidelineopen allclose all
Qualifier:
according to guideline
Guideline:
OECD Guideline 201 (Freshwater Alga and Cyanobacteria, Growth Inhibition Test)
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method C.3 (Algal Inhibition test)
Deviations:
no
GLP compliance:
yes (incl. QA statement)

Test material

Constituent 1
Chemical structure
Reference substance name:
4-isopropylcyclohexanol
EC Number:
225-035-0
EC Name:
4-isopropylcyclohexanol
Cas Number:
4621-04-9
Molecular formula:
C9H18O
IUPAC Name:
4-(propan-2-yl)cyclohexan-1-ol
Test material form:
liquid

Sampling and analysis

Analytical monitoring:
yes
Details on sampling:
For determination of the appropriate test concentrations for the main test, a range-finding test was performed. The nominal test item concentrations tested were 1.0, 10 and 100 mg/L. For this, three replicates per treatment were tested under identical exposure conditions than those applied for the main test. The test medium of the highest concentration of 100 mg/L was stirred until dissolution for 10 minutes at room temperature. The test media of the two lower concentrations were prepared in a series of further dilution steps. Additional samples were prepared to determine the effect of the light on the test item and a possible adsorption of the test item onto the algae.

Test solutions

Vehicle:
no
Details on test solutions:
Based on the range-finding results the following nominal concentrations of FOLROSIA were selected for the main test: 1.0, 3.2, 10, 32 and 100 mg/L. Additionally, a control (test water without test item) was tested in parallel. The test design included three replicates per test concentration and six replicates of the control.

The measured concentrations of the test item FOLROSIA in the test media of the nominal test concentrations of 1.0 to 100 mg/L were between 92 and 106% of the nominal values at the start of the test. Thus, the correct dosage of the test item could be verified. At the end of the test, 82 to 95% of the nominal values were found. The geometric mean measured exposure concentrations were determined to be 0.87, 2.8, 9.3, 30 and 100 mg/L, respectively, at the 1.0, 3.2, 10, 32 and 100 mg/L (nominal) test concentrations.

Test organisms

Test organisms (species):
Pseudokirchneriella subcapitata (previous names: Raphidocelis subcapitata, Selenastrum capricornutum)
Details on test organisms:
The test was started using a nominal algal cell density of 5000 cells/mL. The initial cell density was selected according to the recommendations of the OECD test guideline. The algal cell density in the pre-culture was determined using an electronic particle counter (Coulter Counter, Model Z2).

Study design

Test type:
static
Water media type:
other: Reconstituted test water - AAP medium
Limit test:
no
Total exposure duration:
72 h

Test conditions

Hardness:
15 mg/L as CaCO3
Test temperature:
The water temperature during the test was maintained at 22 °C.
pH:
The pH of the test media was in the range of 7.3 to 7.6 during the test period.
Nominal and measured concentrations:
The geometric mean measured exposure concentrations were determined to be 0.87, 2.8, 9.3, 30 and 100 mg/L, respectively, at the 1.0, 3.2, 10, 32 and 100 mg/L (nominal) test concentrations.

Results and discussion

Effect concentrationsopen allclose all
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
9.3 mg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
growth rate
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
63 mg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
growth rate
Remarks on result:
other: 95% CI: 60 - 66 mg/L
Duration:
72 h
Dose descriptor:
EC10
Effect conc.:
30 mg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
growth rate
Remarks on result:
other: 95% CI: 27 - 33 mg/L
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
35 mg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
other: Yield
Remarks on result:
other: 95% CI: 27 - 46 mg/L
Duration:
72 h
Dose descriptor:
EC10
Effect conc.:
8.3 mg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
other: Yield
Remarks on result:
other: 95% CI: 3.1 - 13 mg/L
Duration:
72 h
Dose descriptor:
NOEC
Effect conc.:
2.8 mg/L
Nominal / measured:
meas. (geom. mean)
Conc. based on:
test mat.
Basis for effect:
other: Yield
Results with reference substance (positive control):
For evaluation of the algal quality and experimental conditions, potassium dichromate is tested as a positive control twice a year to demonstrate satisfactory test conditions. The 72-hour EC50 for growth rate in the reference test IES Study Number 20160277 was 0.9 mg/L (October 2016) and showed that the sensitivity of the test system was within the range recommended by the guideline (72-hour EC50 for the growth rate 0.9 - 1.5 mg/L).

Applicant's summary and conclusion

Validity criteria fulfilled:
yes
Executive summary:

A clear concentration-response relationship was observed for both biological endpoints growth rate and yield during the exposure period.

Based on the results of the study, the :

EC50 (growth rate - 72 hr) = 63 mg/L

EC10 (growth rate - 72 hr) = 30 mg/L

NOEC (growth rate - 72 hr) = 9.3 mg/L

EC50 (yield - 72 hr) = 35 mg/L

EC10 (Yield - 72 hr) = 8.3 mg/L

NOEC (yield - 72 hr) = 2.8 mg/L

.