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Ecotoxicological information

Toxicity to aquatic algae and cyanobacteria

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Reference
Endpoint:
toxicity to aquatic algae and cyanobacteria
Type of information:
(Q)SAR
Adequacy of study:
key study
Study period:
From 2015-09-08 to 2015-09-09
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
Justification for type of information:
1. SOFTWARE
iSafeRat® HA-QSAR toolbox v1.1

2. MODEL (incl. version number)
iSafeRat® holistic HA-QSAR v1.4

3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
c1cccc(CC(C)COC)c1
The water solubility given as input was experimentally measured: 195 mg/L

4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
See attached QMRF

5. APPLICABILITY DOMAIN
See attached QPRF

6. ADEQUACY OF THE RESULT
See attached QPRF
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 201 (Alga, Growth Inhibition Test)
Deviations:
not applicable
Remarks:
(QSAR model)
Principles of method if other than guideline:
The acute toxicity to aquatic algae was determined using a validated QSAR for the Mode of Action in question, based on validated data derived from 72-hour ErC50 tests on algae, for which the concentrations of the test item had been determined by chemical analyses over the test period. The QSAR is a simple linear regression of sub-cooled liquid solubility versus 72-h ErC50 for algae and is valid within the applicability domain defined in the QMRF.
GLP compliance:
no
Specific details on test material used for the study:
- Water solubility: 195 mg/L (from experimental study)
Analytical monitoring:
no
Details on sampling:
Not applicable
Vehicle:
no
Details on test solutions:
Not applicable
Test organisms (species):
other: algae spp.
Details on test organisms:
Not applicable
Test type:
other: QSAR method
Water media type:
freshwater
Limit test:
no
Total exposure duration:
72 h
Remarks on exposure duration:
none
Post exposure observation period:
Not applicable
Hardness:
The QSAR is based on data from studies performed at acceptable hardness to ensure control survival.
Test temperature:
The temperatures varied from approximately 20 to 25 °C depending on the species used to construct the algorithm. This small difference is not expected to contribute to the variability of the ErC50 values found in experimental data.
pH:
The QSAR is based on data from studies performed at acceptable pH between 6.0 - 9.0.
Dissolved oxygen:
The QSAR is based on data from studies performed at acceptable oxygen concentrations (generally >60%).
Salinity:
Not applicable.
Nominal and measured concentrations:
The QSAR is based on data from studies performed using measured concentrations or with acceptable stability.
Details on test conditions:
Not applicable
Reference substance (positive control):
no
Remarks:
QSAR model
Key result
Duration:
72 h
Dose descriptor:
EC50
Effect conc.:
8.5 mg/L
Nominal / measured:
meas. (not specified)
Conc. based on:
test mat.
Basis for effect:
growth rate
Remarks on result:
other: 95% CL: 7.5-9.7 mg/L
Details on results:
The water solubility value given as input to the Ecotox module of the iSafeRat® Holistic HA-QSAR falls within the descriptor domain of the model between log water solubility (in log (mol/L)) of -4.38 to 0.49. Moreover the test substance is attributed to the class of non-polar narcotic compounds (MOA 1).
Results with reference substance (positive control):
Not applicable
Reported statistics and error estimates:
95% CL: 7.5-9.7 mg/L.
QSAR statistical parameters are given in the QMRF and the QPRF

No additional information

Validity criteria fulfilled:
yes
Remarks:
The substance falls into applicability domains of the QSAR model
Conclusions:
The 72-h ErC50 value based on measured concentrations was determined to be 8.5 mg/L with 95%-Confidence Limit between 7.5 and 9.7 mg/L.
Executive summary:

A QSAR prediction (KREATiS, 2015) was performed to assess the inhibition of growth to algae of the test substance. This QSAR has been validated to be compliant with the OECD recommendations for QSAR modelling (OECD, 2004) and predicts the endpoint value which would be expected when testing the substance under experimental conditions in a laboratory following OECD Guideline 201. The criterion predicted was the ErC50 (Median Effective Concentration for specific growth rate), a statistically derived concentration which is expected to cause 50% inhibition of intrinsic rate of growth of the test system within a period of 72 hours.

 

The growth inhibition of algae was determined using a validated QSAR for the Mode of Action in question, (MOA 1, non-polar narcosis). This QSAR is based on validated data for a training set of 40 chemicals derived from 72-hour ErC50 test on algae, for which the concentrations of the test substance had been determined by chemical analyses over the test period. The water solubility of the substance given as input was experimentally measured at 195 mg/L.The substance falls within the applicability domain of the model as demonstrated in the QPRF.

The 72-h ErC50 value based on measured concentrations was determined to be 8.5 mg/L with 95%-Confidence Limit between 7.5 and 9.7 mg/L.

Description of key information

QSAR model, iSafeRat holistic approach v1.4, key study, validity 2:

72h-ErC50 = 8.5 mg/L (95% CL: 7.5 - 9.7 mg/L).

Key value for chemical safety assessment

EC50 for freshwater algae:
8.5 mg/L

Additional information

To assess the toxicity of the registered substance to aquatic algae, one data point is available.

This value (KREATiS, 2015), assessed as a key datapoint, is a QSAR. This QSAR prediction (iSafeRat holistic approach v1.4) was performed on the registered substance, to assess the inhibition of growth to algae of the substance and was also used to predict the toxicity to daphnids. As the toxicity prediction result for daphnids is more conservative than the in vivo result for daphnids, and as the model uses a holistic approach for toxicity determination, this QSAR can be considered fit for purpose for estimating the aquatic algae endpoint, in a conservative way.

The QSAR has been validated to be compliant with the OECD recommendations for QSAR modelling (OECD, 2004) and predicts the endpoint value which would be expected when testing the substance under experimental conditions in a laboratory following OECD Guideline 201. The growth inhibition of algae was determined using a validated QSAR for the Mode of Action in question, (MOA 1, non-polar narcosis). This QSAR is based on validated data for a training set of 40 chemicals derived from 72-hour ErC50 tests on algae, for which the concentrations of the test substance had been determined by chemical analyses over the test period. The water solubility of the substance given as input was experimentally measured (195 mg/L). The substance falls within the applicability domain of the model. The 72-h ErC50 value based on growth rate and measured concentrations was determined to be 8.5 mg/L (95%-Confidence Limit: 7.5 - 9.7 mg/L).

In conclusion, as the same QSAR model was validated for the "short-term toxicity to aquatic invertebrates" endpoint with an experimental study and the results from this prediction was observed to be conservative compared to those obtained from the experimental study, this result can be used for the algae endpoint. Therefore, the 72h-ErC50 value on algae was considered to be 8.5 mg/L (95% CL: 7.5 - 9.7 mg/L).

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