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Ecotoxicological information

Long-term toxicity to fish

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Endpoint:
long-term toxicity to fish, other
Remarks:
(Q)SAR calculated endpoint
Type of information:
(Q)SAR
Adequacy of study:
key study
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:
QSAR prediction: US EPA accepted QSAR method for chemicals properties assessment.
The substance is readily biodegradable and considered to be of low risk to fish.
Qualifier:
according to guideline
Guideline:
other: QSAR
Principles of method if other than guideline:
ECOSAR Program (v1.00)
GLP compliance:
no
Remarks:
not applicable to QSAR models
Analytical monitoring:
not required
Vehicle:
not specified
Test organisms (species):
other: Fish species
Details on test organisms:
no further information
Test type:
other: QSAR model
Water media type:
freshwater
Limit test:
no
Total exposure duration:
30 d
Hardness:
not applicable. QSAR model
Test temperature:
not applicable. QSAR model
pH:
not applicable. QSAR model
Dissolved oxygen:
not applicable. QSAR model
Salinity:
not applicable. QSAR model
Details on test conditions:
SMILES : CCCCCCCCCC
CHEM : Stoddard solvent
CAS Num: 8052-41-3
MOL FOR: C10 H22
MOL WT : 142.29
Log Kow: 5.252 (EPISuite Kowwin v1.68 Estimate)
Log Kow: 5.01 (PhysProp DB exp value - for comparison only)
Melt Pt: -29.70 (deg C, PhysProp DB exp value for Wat Sol est)
Wat Sol: 1.409 (mg/L, EPISuite WSKowwin v1.43 Estimate)
Wat Sol: 0.052 (mg/L, PhysProp DB exp value)
Reference substance (positive control):
no
Duration:
30 d
Dose descriptor:
NOEC
Effect conc.:
0.02 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: (Q)SAR prediction
Remarks on result:
other: toxic , as determined by (Q)SAR
Details on results:
A NOEC value of 0.02 mg/L has been calculated for the effects of the test substance on the mortality of the fish taxonomic group. This result signifies that the test substance is expected to be toxic .

Overview of QSARs estimations onlong-term aquatic toxicity of  Stoddard solvent to fish

 

Method

 

Results

Remarks

Reference

QSAR

estimate

Fish, 96-hr LC50 =0.140 mg/L (ppm)

Fish 30-day ChV = 0.020 mg/L (ppm)

 

Reliable with restrictions,

QSAR estimated data

ECOSAR Program (v1.00)

 

Fish, 96-hr LC50 =0.140mg/L (ppm)

Fish 30-day ChV =0.020mg/L (ppm)

 

 

 

Validity criteria fulfilled:
yes
Remarks:
US EPA accepted QSAR method for chemicals properties assessment.
Conclusions:
A NOEC value of 0.02 mg/L has been calculated for the effects of the test substance on the mortality of the fish taxonomic group. This result signifies that the test substance is expected to be toxic .
The model indicated that Stoddard solvent possess properties indicating a potential hazard for the environment based on nominal loadings.
Executive summary:

The ECOSAR QSAR model predicts that the NOEC for freshwater fish would to be 0.02 mg/l . This result signifies that the test substance is expected to be toxic .

The model indicated that Stoddard solvent possess properties indicating a potential hazard for the environment based on nominal loadings. 

Endpoint:
long-term toxicity to fish, other
Remarks:
(Q)SAR calculated endpoint
Type of information:
(Q)SAR
Adequacy of study:
key study
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:
QSAR prediction: US EPA accepted QSAR method for chemicals properties assessment.
Qualifier:
according to guideline
Guideline:
other: QSAR
Principles of method if other than guideline:
ECOSAR Program (v1.00)
GLP compliance:
no
Remarks:
not applicable to QSAR models
Analytical monitoring:
not required
Vehicle:
not specified
Test organisms (species):
other: Fish species
Details on test organisms:
no further information
Test type:
other: QSAR model
Water media type:
saltwater
Limit test:
no
Total exposure duration:
30 d
Hardness:
not applicable. QSAR model
Test temperature:
not applicable. QSAR model
pH:
not applicable. QSAR model
Dissolved oxygen:
not applicable. QSAR model
Salinity:
not applicable. QSAR model
Details on test conditions:
SMILES : CCCCCCCCCC
CHEM : Stoddard solvent
CAS Num: 8052-41-3
MOL FOR: C10 H22
MOL WT : 142.29
Log Kow: 5.252 (EPISuite Kowwin v1.68 Estimate)
Log Kow: 5.01 (PhysProp DB exp value - for comparison only)
Melt Pt: -29.70 (deg C, PhysProp DB exp value for Wat Sol est)
Wat Sol: 1.409 (mg/L, EPISuite WSKowwin v1.43 Estimate)
Wat Sol: 0.052 (mg/L, PhysProp DB exp value)
Reference substance (positive control):
no
Duration:
30 d
Dose descriptor:
NOEC
Effect conc.:
0.142 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
other: (Q)SAR prediction
Remarks on result:
other: non-toxic at the limit of solubility, as determined by (Q)SAR
Details on results:
A NOEC value of 0.142 mg/L has been calculated for the effects of the test substance on the mortality of the fish taxonomic group. This result signifies that the test substance is not expected to be toxic at the limit of solubility. This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and NOEC is >LoS.

Overview of QSARs estimations onlong-term aquatic toxicity of  Stoddard solvent to fish

 

Method

 

Results

Remarks

Reference

QSAR

estimate

Fish, 96-hr LC50 =0.140 mg/L (ppm)

Fish, 96-hr (SW) LC50 =0.180 mg/L (ppm)

Fish 30-day ChV = 0.020 mg/L (ppm)

Fish (SW) 30-day ChV = 0.142 mg/L (ppm)

 

Reliable with restrictions,

QSAR estimated data

ECOSAR Program (v1.00)

   

Fish, 96-hr LC50 =0.140mg/L (ppm)

Fish, 96-hr (SW) LC50 =0.180mg/L (ppm)

Fish 30-day ChV =0.020mg/L (ppm)

Fish (SW) 30-day ChV = 0.142mg/L (ppm)

 

 

Validity criteria fulfilled:
yes
Remarks:
US EPA accepted QSAR method for chemicals properties assessment.
Conclusions:
A NOEC value of 0.142 mg/L has been calculated for the effects of the test substance on the mortality of the fish taxonomic group. This result signifies that the test substance is not expected to be toxic at the limit of solubility. This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and NOEC is >LoS.
The model indicated that Stoddard solvent possess properties indicating a potential hazard for the environment (acute toxicity for fish, invertebrates, and algae (in the range of 0.1 – 1.0 mg/l) based on nominal loadings.

Executive summary:

The ECOSAR QSAR model predicts that the NOEC for marinewater fish would to be 0.142 mg/l .This result signifies that the test substance is not expected to be toxic at the limit of solubility.This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and NOEC is >LoS.

The model indicated that Stoddard solvent possess properties indicating a potential hazard for the environment (acute toxicity for fish, invertebrates, and algae (in the range of 0.1 – 1.0 mg/l) based on nominal loadings.

 

Endpoint:
fish early-life stage toxicity
Type of information:
other: Published data
Adequacy of study:
weight of evidence
Study period:
112 days
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
study well documented, meets generally accepted scientific principles, acceptable for assessment
Justification for type of information:
Published data in readily available literature. A 112 days chronic study was conducted with CAS RN 8008-20-6, using rainbow trout, Oncorhynchus mykiss.
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 210 (Fish, Early-Life Stage Toxicity Test)
Principles of method if other than guideline:
A chronic bioassay test procedure was run in a flow-through experiment, starting with rainbow trout eggs which were exposed to 4 concentrations of the water-soluble fraction (WSF) of jet fuel JP-8, corresponding to 1.4 to 8.0 mg/l of dissolved hydrocarbons.
Hatching was complete by day 4 and tests continued to day 112 using the same WSF dilutions.
GLP compliance:
not specified
Analytical monitoring:
yes
Details on sampling:
Fish were exposed to the water soluble fraction (WSF) of JP-8 in static acute bioassays and continuous-flow bioassays of approx. 4 months duration.
Vehicle:
yes
Details on test solutions:
Test treatments were prepared as WAFs in sealed test vessels to contain the volatile components.
Test organisms (species):
Oncorhynchus mykiss (previous name: Salmo gairdneri)
Details on test organisms:
Rainbow trout (Oncorhynchus mykiss)
Test type:
flow-through
Water media type:
freshwater
Limit test:
no
Total exposure duration:
112 d
Hardness:
The water used in this study had a total hardness range of 170-180 mg/l as CaCO3
Test temperature:
Water temperature was 15 to 28° C
The toxicity of JP-8 to cold and warm water fish was investigated to help define the impact on fresh water species
pH:
7.3–9.1
Dissolved oxygen:
average: 6.0 mg/L (4.4 to 7.2 mg/L)
Salinity:
N.A.
Nominal and measured concentrations:
4 concentrations of the water-soluble fraction (WSF) of jet fuel JP-8, corresponding to 1.4 to 8.0 mg/l of dissolved hydrocarbons.
Reference substance (positive control):
no
Duration:
112 d
Dose descriptor:
NOEC
Effect conc.:
< 1.4 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Duration:
112 d
Dose descriptor:
LOEC
Effect conc.:
ca. 1.4 mg/L
Nominal / measured:
nominal
Conc. based on:
test mat.
Basis for effect:
growth rate
Details on results:
The NOEC for the study was < 1.4 mg/l, and was based on the growth rate of young fish.
The LOEC was 1.4mg/l.

Rainbow trout exposed to a dissolved hydrocarbon concentration of 1.4 mg/l grew at a rate significantly lower than the controls. Mortality of fish exposed to concentrations over 1.4 mg/l was significantly greater than that of the controls.

The extent of egg hatching was not affected at a concentration of 8.0 mg/l of dissolved hydrocarbons.

Validity criteria fulfilled:
yes
Conclusions:
112 day NOEC values < 1. 4 mg/L were determined for the effects of the test substance on growth of the larvae of freshwater fish Rainbow trout (O. mykiss) .
The LOECwas 1.4mg/l
Executive summary:

The NOEC for the study was < 1.4 mg/l, and was based on the growth rate of young fish.

The LOEC was 1.4mg/l.

Description of key information

The ECOSAR QSAR model predicts that the NOEC for freshwater fish would to be 0.02 mg/l

The ECOSAR QSAR model predicts that the NOEC for marinewater fish would to be 0.142 mg/l

112 day NOEC values < 1. 4 mg/L were determined for the effects of the test substance on growth of the larvae of freshwater fish Rainbow trout (O. mykiss) .

Key value for chemical safety assessment

Fresh water fish

Fresh water fish
Effect concentration:
1.4 mg/L

Marine water fish

Marine water fish
Effect concentration:
0.142 mg/L

Additional information