Fir, Abies sibirica, ext.

Short-term toxicity to aquatic invertebrates

Link to relevant study record(s)

Reference

Reference 1

Endpoint:

short-term toxicity to aquatic invertebrates

Type of information:

(Q)SAR

Adequacy of study:

supporting study

Study period:

2014-05-23 to 2014-05-23

Reliability:

2 (reliable with restrictions)

Rationale for reliability incl. deficiencies:

other: QSAR value. The substance falls into the applicability domains of the QSAR model.

Justification for type of information:

QSAR prediction: migrated from IUCLID 5.6

Qualifier:

equivalent or similar to guideline

Guideline:

OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)

Deviations:

yes

Remarks:

QSAR model

Principles of method if other than guideline:

The acute toxicity to aquatic invertebrates was determined using a validated QSAR for the Mode of Action in question, based on validated data derived from 48-hour EC50 tests on daphnia, 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 48-h EC50 for daphnia and is valid within the applicability domain defined in the QMRF.

GLP compliance:

no

Specific details on test material used for the study:

Details on properties of test surrogate or analogue material (migrated information):
not applicable

Analytical monitoring:

no

Details on sampling:

not applicable

Vehicle:

no

Details on test solutions:

not applicable

Test organisms (species):

Daphnia sp.

Details on test organisms:

not applicable

Test type:

other: QSAR

Water media type:

freshwater

Limit test:

no

Total exposure duration:

48 h

Remarks on exposure duration:

48h-EC50

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 QSAR is based on data from studies performed at between 14 - 25 °C (depending on the species considered)

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:

The QSAR is based on data from studies performed on freshwater species

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

Duration:

48 h

Dose descriptor:

EC50

Effect conc.:

0.57 mg/L

Conc. based on:

test mat.

Basis for effect:

mobility

Remarks on result:

other: 95% CL [0.34-0.94]

Details on results:

not applicable

Results with reference substance (positive control):

not applicable

Reported statistics and error estimates:

95% CL [0.34-0.94]
QSAR statistical parameters are given in the QMRF and the QPRF

no data

Validity criteria fulfilled:

yes

Remarks:

The substance falls into the applicability domains of the QSAR model.

Conclusions:

48h-EC50 for Δ-3-carene = 0.57 mg test item/L with 95% Confidence Limit between 0.34 and 0.94 mg test item/L.

Executive summary:

The acute toxicity to daphnia was determined using a validated QSAR for the Mode of Action in question, based on validated data derived from 48-hour EC50 tests on daphnia, 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 48-h EC50 for daphnia and is valid within the applicability domain defined in the QMRF.

The acute toxicity to daphnia of Δ-3-carene has been investigated using a QSAR model that predicts daphnia mortality in an OECD 202 study. Δ-3-carene falls within the applicability domain of the model as demonstrated in the QPRF.

The 48-h EC50 was 0.57 mg test material/L with 95%-Confidence Limit between 0.34 and 0.94 mg test material/L. EC50 were based on mobility. 

Based on the results of this study, Δ-3-carene would be classified as acute 1 to aquatic organisms in accordance with the classification of the CLP.

This toxicity study is acceptable and can be used for that endpoint.

 

Results Synopsis

Test Type: QSAR model

LC50: 0.57 mg test material/L 95%-C.L.: 0.34 to 0.94 mg test material/L

Reference 2

Endpoint:

short-term toxicity to aquatic invertebrates

Type of information:

(Q)SAR

Adequacy of study:

supporting study

Study period:

2014-05-20 to 2014-05-23

Reliability:

2 (reliable with restrictions)

Rationale for reliability incl. deficiencies:

other: QSAR value. The substance falls into the applicability domains of the QSAR model.

Justification for type of information:

QSAR prediction: migrated from IUCLID 5.6

Qualifier:

equivalent or similar to guideline

Guideline:

OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)

Deviations:

yes

Remarks:

QSAR model

Principles of method if other than guideline:

The acute toxicity to aquatic invertebrates was determined using a validated QSAR for the Mode of Action in question, based on validated data derived from 48-hour EC50 tests on daphnia, 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 48-h EC50 for daphnia and is valid within the applicability domain defined in the QMRF.

GLP compliance:

no

Specific details on test material used for the study:

Details on properties of test surrogate or analogue material (migrated information):
not applicable

Analytical monitoring:

no

Details on sampling:

not applicable

Vehicle:

no

Details on test solutions:

not applicable

Test organisms (species):

Daphnia sp.

Details on test organisms:

not applicable

Test type:

other: QSAR

Water media type:

freshwater

Limit test:

no

Total exposure duration:

48 h

Remarks on exposure duration:

48h-EC50

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 QSAR is based on data from studies performed at between 14 - 25 °C (depending on the species considered)

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:

The QSAR is based on data from studies performed on freshwater species

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

Duration:

48 h

Dose descriptor:

EC50

Effect conc.:

1.37 mg/L

Conc. based on:

test mat.

Basis for effect:

mobility

Remarks on result:

other: 95% CL [0.91-2.07]

Details on results:

not applicable

Results with reference substance (positive control):

not applicable

Reported statistics and error estimates:

95% CL [0.91-2.07]
QSAR statistical parameters are given in the QMRF and the QPRF

no data

Validity criteria fulfilled:

yes

Remarks:

The substance falls into the applicability domains of the QSAR model.

Conclusions:

48h-EC50 for limonene = 1.37 mg test item/L with 95% Confidence Limit between 0.91 and 2.07 mg test item/L.

Executive summary:

The acute toxicity to daphnia was determined using a validated QSAR for the Mode of Action in question, based on validated data derived from 48-hour EC50 tests on daphnia, 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 48-h EC50 for daphnia and is valid within the applicability domain defined in the QMRF.

The acute toxicity to daphnia of limonene has been investigated using a QSAR model that predicts daphnia mortality in an OECD 202 study. Limonene falls within the applicability domain of the model as demonstrated in the QPRF.

The 48-h EC50 was 1.37 mg test material/L with 95%-Confidence Limit between 0.91 and 2.07 mg test material/L. EC50 were based on mobility. 

Based on the results of this study, limonene would not be classified as acute 1 to aquatic organisms in accordance with the classification of the CLP.

This toxicity study is acceptable and can be used for that endpoint.

 

Results Synopsis

Test Type: QSAR model

LC50: 1.37 mg test material/L 95%-C.L.: 0.91 to 2.07 mg test material/L

Reference 3

Endpoint:

short-term toxicity to aquatic invertebrates

Type of information:

experimental study

Adequacy of study:

supporting study

Study period:

1989

Reliability:

2 (reliable with restrictions)

Rationale for reliability incl. deficiencies:

other: see 'Remark'

Remarks:

Study conducted similarly to OECD guideline 202 with minor deviations: no data on acclimation period, feeding pattern and reference substance. There are no details on the solubility data of the substance and this value is not in accordance with the solubility determined in a recent study conducted according to the OECD guideline. In fact, results show that there is no toxicity at the solubilit limit. Mortality at higher nominal rates could be explain by physical effects.

Reason / purpose for cross-reference:

reference to same study

Qualifier:

equivalent or similar to guideline

Guideline:

OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)

Deviations:

yes

Remarks:

no data on acclimation period, feeding pattern and reference substance

GLP compliance:

not specified

Specific details on test material used for the study:

Details on properties of test surrogate or analogue material (migrated information):
No data

Analytical monitoring:

yes

Details on sampling:

- Concentrations: 0, 390, 780, 1170, 1560 or 1950 µg/L
- Sampling time: 0, 24 and 48 hours

Vehicle:

yes

Details on test solutions:

PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: Test solutions was provided as liquid/liquid saturation units by adding excess of test chemical in 14 L of Lake Superior water
- Controls: Dilution water
- Chemical name of vehicle: Water
- Concentration of vehicle in test medium: Stock (1950 µg/L liq-liq equil.)

Test organisms (species):

Daphnia magna

Details on test organisms:

TEST ORGANISM
- Common name: Water flea
- Source: ERL-Duluth, USA
- Age at study initiation: < 24 hours

Test type:

flow-through

Water media type:

freshwater

Limit test:

no

Total exposure duration:

48 h

Post exposure observation period:

None

Hardness:

43.8 ± 1.2 mg/L CaCO3

Test temperature:

20.1 ± 0.4 °C

pH:

7.9 ± 0.05

Dissolved oxygen:

8.2 ± 0.2 mg O2/L

Salinity:

No data

Nominal and measured concentrations:

Nominal concentrations: 0, 390, 780, 1170, 1560 and 1950 µg/L

Details on test conditions:

TEST SYSTEM
- Test vessel: Six crystallizing dishes were used as test chambers in the electronic diluter with tank volumes of 250 mL; test solution depth: 4-5 cm
- Type (delete if not applicable): Closed; stainless steel screen enclosures (forty mesh) were placed in each chamber for the daphnia exposures
- Type of flow-through: Electronic diluter
- Renewal rate of test solution (frequency/flow rate): Flow rates of 21 mL/min to each tank provided concentrations of 244-1760 µg/L
- No. of organisms per vessel: 15
- No. of vessels per concentration (replicates): One
- No. of vessels per vehicle control (replicates): One

TEST MEDIUM / WATER PARAMETERS
- Source of dilution water: Lake Superior water
- Preparation of dilution water: Water was passed through sand filters, ultraviolet sterilizers and 55 µm fibre filter. Test waters were then aerated and heated at 20 ± 1 °C
- Alkalinity: 36.2 ± 0.3 mg/L CaCO3
- Intervals of water quality measurement: Tank temperatures (°C), dissolved oxygen (mg/L) and pH were measured daily in each of the test chambers where test organisms were still alive

OTHER TEST CONDITIONS
- Photoperiod: 16 hour/day light cycle; cool white fluorescent light
- Light intensity: 12-28 lumens

EFFECT PARAMETERS MEASURED (with observation intervals if applicable):
- Mortalities or other effects were observed at 24 and 48 hours

Reference substance (positive control):

no

Duration:

48 h

Dose descriptor:

EC50

Effect conc.:

1 250 µg/L

Nominal / measured:

meas. (arithm. mean)

Conc. based on:

test mat.

Basis for effect:

mobility

Remarks on result:

other: 1150-1360 µg/L

Details on results:

- Mortality or behavioural abnormalities: No mortality occurred during the test, however, organisms showed signs of stress at approximately 24 hour, failed to swim throughout the water column and remained on the bottoms of the test chambers. Because the highest chamber concentration was measured near water solubility (approximately 2100 µg/L), the test was not repeated.
- LC50 values were not determined due to limited mortality
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: Measured concentrations were lower than nominal concentrations due to volatility.

Results with reference substance (positive control):

Not applicable

Reported statistics and error estimates:

- EC50 was calculated using the corrected average of the analyzed tank concentrations and the Trimmed Spearman-Karber Method (Hamilton et al., 1977).
- Mean toxicant concentrations used in the calculations were corrected for analytical spike recoveries

Table 2: Effects

 

Hour	Control (0 µg/L)	A (390 µg/L)	B (780 µg/L)	C (1170 µg/L)	D (1560 µg/L)	E (1950 µg/L)
Initial	15	15	15	15	15	15
24						15
48					5	15

Validity criteria fulfilled:

yes

Remarks:

mortality in control < 10% (no immobilisation observed); dissolved oxygen concentration > 3 mg O2/L

Conclusions:

Under the test conditions, no effects were observed at the solubility limit.

Executive summary:

In an acute aquatic toxicity study performed similarly to OECD guideline 202, groups (15/dose) of Daphnia magna was exposed to β-pinene at concentrations of 0, 390, 780, 1170, 1560 and 1950 µg/L (nominal) for 48 hours under flow-through conditions. Mortality and effects were observed at 24 and 48 hours.

 

No mortality occurred during the test, however, organisms showed signs of stress at approximately 24 hour, failed to swim throughout the water column and remained on the bottoms of the test chambers.

The study was conducted similarly to OECD guideline 202 but there are no details on the solubility data of the substance and this value is not in accordance with the solubility determined in a recent study conducted according to the OECD guideline. In fact, results show that there is no toxicity at the solubilit limit. Mortality at higher nominal rates could be explain by physical effects.

Reference 4

Endpoint:

short-term toxicity to aquatic invertebrates

Type of information:

(Q)SAR

Adequacy of study:

supporting study

Study period:

2014-05-23 to 2014-05-23

Reliability:

2 (reliable with restrictions)

Rationale for reliability incl. deficiencies:

other: QSAR value. The substance falls into the applicability domains of the QSAR model.

Justification for type of information:

QSAR prediction: migrated from IUCLID 5.6

Qualifier:

equivalent or similar to guideline

Guideline:

OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)

Deviations:

yes

Remarks:

QSAR model

Principles of method if other than guideline:

The acute toxicity to aquatic invertebrates was determined using a validated QSAR for the Mode of Action in question, based on validated data derived from 48-hour EC50 tests on daphnia, 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 48-h EC50 for daphnia and is valid within the applicability domain defined in the QMRF.

GLP compliance:

no

Specific details on test material used for the study:

Details on properties of test surrogate or analogue material (migrated information):
not applicable

Analytical monitoring:

no

Details on sampling:

not applicable

Vehicle:

no

Details on test solutions:

not applicable

Test organisms (species):

Daphnia sp.

Details on test organisms:

not applicable

Test type:

other: QSAR

Water media type:

freshwater

Limit test:

no

Total exposure duration:

48 h

Remarks on exposure duration:

48h-EC50

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 QSAR is based on data from studies performed at between 14 - 25 °C (depending on the species considered)

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:

The QSAR is based on data from studies performed on freshwater species

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

Duration:

48 h

Dose descriptor:

EC50

Effect conc.:

0.8 mg/L

Conc. based on:

test mat.

Basis for effect:

mobility

Remarks on result:

other: 95% CL [0.50-1.28]

Details on results:

not applicable

Results with reference substance (positive control):

not applicable

Reported statistics and error estimates:

95% CL [0.50-1.28]
QSAR statistical parameters are given in the QMRF and the QPRF

no data

Validity criteria fulfilled:

yes

Remarks:

The substance falls into the applicability domains of the QSAR model.

Conclusions:

48h-EC50 for β-phellandrene = 0.80 mg test item/L with 95% Confidence Limit between 0.50 and 1.28 mg test item/L.

Executive summary:

The acute toxicity to daphnia was determined using a validated QSAR for the Mode of Action in question, based on validated data derived from 48-hour EC50 tests on daphnia, 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 48-h EC50 for daphnia and is valid within the applicability domain defined in the QMRF.

The acute toxicity to daphnia of β-phellandrene has been investigated using a QSAR model that predicts daphnia mortality in an OECD 202 study. β-phellandrene falls within the applicability domain of the model as demonstrated in the QPRF.

The 48-h EC50 was 0.80 mg test material/L with 95%-Confidence Limit between 0.50 and 1.28 mg test material/L. EC50 were based on mobility. 

Based on the results of this study, Camphene would be classified as acute 1 to aquatic organisms in accordance with the classification of the CLP.

This toxicity study is acceptable and can be used for that endpoint.

 

Results Synopsis

Test Type: QSAR model

LC50: 0.80 mg test material/L 95%-C.L.: 0.50 to 1.28 mg test material/L

Reference 5

Endpoint:

short-term toxicity to aquatic invertebrates

Type of information:

(Q)SAR

Adequacy of study:

supporting study

Study period:

2014-05-23 to 2014-05-23

Reliability:

2 (reliable with restrictions)

Rationale for reliability incl. deficiencies:

other: QSAR value. The substance falls into the applicability domains of the QSAR model.

Justification for type of information:

QSAR prediction: migrated from IUCLID 5.6

Qualifier:

equivalent or similar to guideline

Guideline:

OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)

Deviations:

yes

Remarks:

QSAR model

Principles of method if other than guideline:

The acute toxicity to aquatic invertebrates was determined using a validated QSAR for the Mode of Action in question, based on validated data derived from 48-hour EC50 tests on daphnia, 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 48-h EC50 for daphnia and is valid within the applicability domain defined in the QMRF.

GLP compliance:

no

Specific details on test material used for the study:

Details on properties of test surrogate or analogue material (migrated information):
not applicable

Analytical monitoring:

no

Details on sampling:

not applicable

Vehicle:

no

Details on test solutions:

not applicable

Test organisms (species):

Daphnia sp.

Details on test organisms:

not applicable

Test type:

other: QSAR

Water media type:

freshwater

Limit test:

no

Total exposure duration:

48 h

Remarks on exposure duration:

48h-EC50

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 QSAR is based on data from studies performed at between 14 - 25 °C (depending on the species considered)

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:

The QSAR is based on data from studies performed on freshwater species

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

Duration:

48 h

Dose descriptor:

EC50

Effect conc.:

7.28 mg/L

Conc. based on:

test mat.

Basis for effect:

mobility

Remarks on result:

other: 95% CL [4.56-11.64]

Details on results:

not applicable

Results with reference substance (positive control):

not applicable

Reported statistics and error estimates:

95% CL [4.56-11.64]
QSAR statistical parameters are given in the QMRF and the QPRF

no data

Validity criteria fulfilled:

yes

Remarks:

The substance falls into the applicability domains of the QSAR model.

Conclusions:

48h-EC50 for Bornyl acetate = 7.28 mg test item/L with 95% Confidence Limit between 4.56 and 11.64 mg test item/L.

Executive summary:

The acute toxicity to daphnia was determined using a validated QSAR for the Mode of Action in question, based on validated data derived from 48-hour EC50 tests on daphnia, 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 48-h EC50 for daphnia and is valid within the applicability domain defined in the QMRF.

The acute toxicity to daphnia of Bornyl acetate has been investigated using a QSAR model that predicts daphnia mortality in an OECD 202 study. Bornyl acetate falls within the applicability domain of the model as demonstrated in the QPRF.

The 48-h EC50 was 7.28 mg test material/L with 95%-Confidence Limit between 4.56 and 11.64 mg test material/L. EC50 were based on mobility. 

Based on the results of this study, limonene would not be classified as acute 1 to aquatic organisms in accordance with the classification of the CLP.

This toxicity study is acceptable and can be used for that endpoint.

 

Results Synopsis

Test Type: QSAR model

LC50: 7.28 mg test material/L 95%-C.L.: 4.56 to 11.64 mg test material/L

Reference 6

Endpoint:

short-term toxicity to aquatic invertebrates

Type of information:

experimental study

Adequacy of study:

supporting study

Study period:

1989

Reliability:

2 (reliable with restrictions)

Rationale for reliability incl. deficiencies:

other: Study conducted similarly to OECD guideline 202 with minor deviations: no data on acclimation period, feeding pattern and reference substance.

Reason / purpose for cross-reference:

reference to same study

Qualifier:

equivalent or similar to guideline

Guideline:

OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)

Deviations:

yes

Remarks:

no data on acclimation period, feeding pattern and reference substance

GLP compliance:

not specified

Specific details on test material used for the study:

Details on properties of test surrogate or analogue material (migrated information):
Not applicable

Analytical monitoring:

yes

Details on sampling:

- Concentrations: 0, 124, 248, 372, 496 or 620 µg/L
- Sampling time: 0, 24 and 48 hours

Vehicle:

yes

Details on test solutions:

PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: Test solutions was provided as liquid/liquid saturation units by adding excess of test chemical in 14 L of Lake Superior water
- Controls: Dilution water
- Chemical name of vehicle: Water
- Concentration of vehicle in test medium: Stock (620 µg/L liq-liq equil.)

Test organisms (species):

Daphnia magna

Details on test organisms:

TEST ORGANISM
- Common name: Water flea
- Source: ERL-Duluth, USA
- Age at study initiation: < 24 hours

Test type:

flow-through

Water media type:

freshwater

Limit test:

no

Total exposure duration:

48 h

Post exposure observation period:

None

Hardness:

45.4 ± 0.2 mg/L CaCO3

Test temperature:

20.2 ± 0.2 °C

pH:

7.8 ± 0.09

Dissolved oxygen:

7.8 ± 0.4 mg O2/L

Salinity:

No data

Nominal and measured concentrations:

Nominal concentrations: 0, 124, 248, 372, 496 and 620 µg/L

Details on test conditions:

TEST SYSTEM
- Test vessel: Six crystallizing dishes were used as test chambers in the electronic diluter with tank volumes of 200 mL; test solution depth: 4-5 cm
- Type (delete if not applicable): Closed; stainless steel screen enclosures (forty mesh) were placed in each chamber for the daphnia exposures
- Type of flow-through: Electronic diluter
- Renewal rate of test solution (frequency/flow rate): Single tank exposures were conducted at reduced flow rates (< 7 mL/min) so that a higher concentration could be attained; two additional toxicity tests were completed using the single-cell toxicity screening system: first test utilized a 10 mL/min flow rate into the chamber, while the second test was set at 1 mL/min.
- No. of organisms per vessel: 15
- No. of vessels per concentration (replicates): One
- No. of vessels per vehicle control (replicates): One

TEST MEDIUM / WATER PARAMETERS
- Source of dilution water: Lake Superior water
- Preparation of dilution water: Water was passed through sand filters, ultraviolet sterilizers and 55 µm fibre filter. Test waters were then aerated and heated at 20 ± 1 °C
- Alkalinity: 42.9 ± 0.1 mg/L CaCO3
- Intervals of water quality measurement: Tank temperatures (°C), dissolved oxygen (mg/L) and pH were measured daily in each of the test chambers where test organisms were still alive

OTHER TEST CONDITIONS
- Photoperiod: 16 hours/day light cycle; cool white fluorescent light
- Light intensity: 12-28 lumens

EFFECT PARAMETERS MEASURED (with observation intervals if applicable):
- Mortalities or other effects were observed at 24 and 48 hours

Reference substance (positive control):

no

Duration:

48 h

Dose descriptor:

LC50

Effect conc.:

ca. 1 440 µg/L

Nominal / measured:

not specified

Conc. based on:

test mat.

Basis for effect:

mortality

Details on results:

- An approximate LC50 value of 1440 µg/L was calculated based on one mortality in the first test and total mortality in the second test
- EC50 values were not obtained

Results with reference substance (positive control):

Not applicable

Reported statistics and error estimates:

- LC50/EC50 was calculated using the corrected average of the analyzed tank concentrations and the Trimmed Spearman-Karber Method (Hamilton et al., 1977).
- Mean toxicant concentrations used in the calculations were corrected for analytical spike recoveries

Table 2: Mortalities

 

Hour	Control (0 µg/L)	A (124 µg/L)	B (248 µg/L)	C (372 µg/L)	D (496 µg/L)	E (620 µg/L)
Initial	15	15	15	15	15	15
48 (Deads)	0	0	0	0	0	2

 

 

Table 2: Effects

 

Hour	Control (0 µg/L)	A (124 µg/L)	B (248 µg/L)	C (372 µg/L)	D (496 µg/L)	E (620 µg/L)
Initial	15	15	15	15	15	15
48 (Effects)	0	0	0	0	0	2

Validity criteria fulfilled:

yes

Remarks:

mortality in control < 10% (no immobilisation observed); dissolved oxygen concentration > 3 mg O2/L

Conclusions:

Under the test conditions, an approximate LC50 value of 1440 µg/L was calculated based on one mortality in the first test and total mortality in the second test.

Executive summary:

In an acute aquatic toxicity study performed similarly to OECD guideline 202, groups (15/dose) of Daphnia magna were exposed to (+)-alpha pinene at concentrations of 0, 124, 248, 372, 496 and 620 µg/L (nominal) for 48 hours under flow-through conditions. Mortality and effects were observed at 24 and 48 hours.

An approximate EC50 value of 1440 µg/L was calculated based on one mortality in the first test and total mortality in the second test. EC50 was not obtained.

Reference 7

Endpoint:

short-term toxicity to aquatic invertebrates

Type of information:

(Q)SAR

Adequacy of study:

supporting study

Study period:

2014-05-23 to 2014-05-23

Reliability:

2 (reliable with restrictions)

Rationale for reliability incl. deficiencies:

other: QSAR value. The substance falls into the applicability domains of the QSAR model.

Justification for type of information:

QSAR prediction: migrated from IUCLID 5.6

Qualifier:

equivalent or similar to guideline

Guideline:

OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)

Deviations:

yes

Remarks:

QSAR model

Principles of method if other than guideline:

The acute toxicity to aquatic invertebrates was determined using a validated QSAR for the Mode of Action in question, based on validated data derived from 48-hour EC50 tests on daphnia, 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 48-h EC50 for daphnia and is valid within the applicability domain defined in the QMRF.

GLP compliance:

no

Specific details on test material used for the study:

Details on properties of test surrogate or analogue material (migrated information):
not applicable

Analytical monitoring:

no

Details on sampling:

not applicable

Vehicle:

no

Details on test solutions:

not applicable

Test organisms (species):

Daphnia sp.

Details on test organisms:

not applicable

Test type:

other: QSAR

Water media type:

freshwater

Limit test:

no

Total exposure duration:

48 h

Remarks on exposure duration:

48h-EC50

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 QSAR is based on data from studies performed at between 14 - 25 °C (depending on the species considered)

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:

The QSAR is based on data from studies performed on freshwater species

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

Duration:

48 h

Dose descriptor:

EC50

Effect conc.:

0.56 mg/L

Conc. based on:

test mat.

Basis for effect:

mobility

Remarks on result:

other: 95% CL [0.33-0.95]

Details on results:

not applicable

Results with reference substance (positive control):

not applicable

Reported statistics and error estimates:

95% CL [0.33-0.95]
QSAR statistical parameters are given in the QMRF and the QPRF

no data

Validity criteria fulfilled:

yes

Remarks:

The substance falls into the applicability domains of the QSAR model.

Conclusions:

48h-EC50 for camphene = 0.56 mg test item/L with 95% Confidence Limit between 0.33 and 0.95 mg test item/L.

Executive summary:

The acute toxicity to daphnia was determined using a validated QSAR for the Mode of Action in question, based on validated data derived from 48-hour EC50 tests on daphnia, 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 48-h EC50 for daphnia and is valid within the applicability domain defined in the QMRF.

The acute toxicity to daphnia of camphene has been investigated using a QSAR model that predicts daphnia mortality in an OECD 202 study. Camphene falls within the applicability domain of the model as demonstrated in the QPRF.

The 48-h EC50 was 0.57 mg test material/L with 95%-Confidence Limit between 0.34 and 0.94 mg test material/L. EC50 were based on mobility. 

Based on the results of this study, Camphene would be classified as acute 1 to aquatic organisms in accordance with the classification of the CLP.

This toxicity study is acceptable and can be used for that endpoint.

 

Results Synopsis

Test Type: QSAR model

LC50: 0.56 mg test material/L 95%-C.L.: 0.33 to 0.95 mg test material/L

Reference 8

Endpoint:

short-term toxicity to aquatic invertebrates

Type of information:

calculation (if not (Q)SAR)

Remarks:

Migrated phrase: estimated by calculation

Adequacy of study:

key study

Study period:

2014-05-23 to 2014-05-26

Reliability:

2 (reliable with restrictions)

Rationale for reliability incl. deficiencies:

other: Calculation method is used ; calculation method applicable for the endpoint

Qualifier:

equivalent or similar to guideline

Guideline:

OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)

Deviations:

yes

Remarks:

calculation method

Principles of method if other than guideline:

The acute toxicity to daphnia was determined using a validated QSAR for the Mode of Action in question. The first step of the iSafeRat mixture toxicity calculation employs phase equilibrium thermodynamics in order to determine the concentrations of each constituent within the WAF. This fraction equates to the analyzable fraction of a WAF study.
Within the WAF, the constituents also partition between themselves further reducing the bioavailable fraction and thus the toxicity of the mixture compared to the individual constituents. In the calculation the second step is to remove this non-bioavailable fraction.
The final step is to determine the truly bioavailable fraction of the WAF per constituent. The EC50s of each constituent are already known from literature or calculated using the iSafeRat QSAR model. Each value and calculation has been included as a supporting study in the IUCLID. An additivity approach (based on Chemical Activity of each constituent) is used in order to calculate the Effective Loading rate of the WAF.
The method has been validated using data derived from 48-hour EC50 tests on aquatic invertebrates, for which the concentrations of the test item had been determined by chemical analyses over the test period. Further to this the effective loading rate of the WAF is determined by using a series of calculation steps using phase equilibrium thermodynamics and excluding the non-bioavailable fraction.

GLP compliance:

no

Specific details on test material used for the study:

Details on properties of test surrogate or analogue material (migrated information):
not applicable

Analytical monitoring:

no

Details on sampling:

not applicable

Vehicle:

no

Details on test solutions:

not applicable

Test organisms (species):

Daphnia sp.

Details on test organisms:

not applicable

Test type:

other: calculation method

Water media type:

freshwater

Limit test:

no

Total exposure duration:

48 h

Remarks on exposure duration:

48h-EL50 (effective loading rate of WAF)

Post exposure observation period:

not applicable

Hardness:

Hardness is not a necessary component of the WAF calculation

Test temperature:

The Temperature is not a necessary component of the WAF calculation but extremely low or high temperatures could influence the solubility of certain constituents. Therefore, the calculation method is considered acceptable to determine EL50s for daphnia between 12 and 28°C.

pH:

The pH is not a necessary component of the WAF calculation

Dissolved oxygen:

The oxygen concentration is not a necessary component of the WAF calculation

Salinity:

Salinity is not a necessary component of the WAF calculation. However as the fish QSAR for the constituents calculation was based on data from freshwater studies, the resulting calculation is considered valid for freshwater organisms

Nominal and measured concentrations:

The calculation determines measured concentrations

Details on test conditions:

calculation method

Reference substance (positive control):

not required

Duration:

48 h

Dose descriptor:

EL50

Effect conc.:

3.6 mg/L

Conc. based on:

test mat.

Basis for effect:

mobility

Duration:

48 h

Dose descriptor:

EL50

Effect conc.:

2.7 mg/L

Conc. based on:

test mat.

Basis for effect:

mobility

Details on results:

not applicable

Results with reference substance (positive control):

not applicable

Reported statistics and error estimates:

not applicable

Table 1: Expected concentrations at this 48h-EL50 (composition 1: typical composition)

constituents	concentration in the WAF (mg.L-1)
limonene	0.84
α-pinene	0.55
β-pinene	0.13
Δ-3-carene	0.12
camphene	0.75
bornyl acetate	0.59
β-phellandrene	0.13

Table 2: Expected concentrations at this 48h-EL50 (composition 2: theoretical worst case composition)

constituents	concentration in the WAF (mg.L-1)
limonene	0.68
α-pinene	0.54
β-pinene	0.22
Δ-3-carene	0.12
myrcene	0.03
camphene	0.81
bornyl acetate	0.27
β-phellandrene	0.04

Validity criteria fulfilled:

yes

Conclusions:

48h-EL50 for typical composition of Pine needle oil (Pine, Abies siberica, ext.) - China = 3.6 mg test item /L and 48h-EL50 for theoretical worst case composition of myrtle oil = 2.7 mg test item/L

Executive summary:

Pine needle oil (Pine,Abies siberica, ext.) – China is a Natural Complex Substance (UVCB) with a well-defined composition for which the relative percentage and its reported variation of each constituent is known. Its acute toxicity to aquatic invertebrate property has been investigated using an in-house calculation method that replaces an OECD 202 study and guideline for Testing of Chemicals No. 23 (i.e. WAF conditions). Two compositions have been investigated, the “typical” composition proposed in the SIP and a theoretical worst case composition, derived from data supplied in the SIP that maximizes the concentration of the most toxic constituents.

The first step of the iSafeRat mixture toxicity calculation employs phase equilibrium thermodynamics in order to determine the concentrations of each constituent within the WAF. This fraction equates to the analysable fraction of a WAF study.

Within the WAF, the constituents also partition between themselves further reducing the bioavailable fraction and thus the toxicity of the mixture compared to the individual constituents. In the calculation the second step is to remove this non-bioavailable fraction.

The final step is to determine the truly bioavailable fraction of the WAF per constituent. The EC50s of each constituent are already known from literature or calculated using the iSafeRat QSAR model. Each value and calculation has been included as a supporting study in the IUCLID. An additivity approach (based on Chemical Activity of each constituent) is used in order to calculate the Lethal Loading of the WAF.

The 48-h EL50 was 3.6 mg test material/L for the typical composition ofPine needle oil (Pine,Abies siberica, ext.) – China, and the 48-h EL50 was 2.7 mg test material/L for the theoretical worst case composition. EL50 were based on mortality. 

Based on the results of this study,Pine needle oil (Pine,Abies siberica, ext.) – China would not be classified as acute 1 to aquatic organisms in accordance with the classification of the CLP.

This toxicity study is acceptable and can be used for that endpoint.

 

Results Synopsis

Test Type: Calculation method

EL50: 3.6 mg test material/L for typical composition

EL50: 2.7 mg test material/L for theoretical worst case composition

Reference 9

Endpoint:

short-term toxicity to aquatic invertebrates

Type of information:

calculation (if not (Q)SAR)

Remarks:

Migrated phrase: estimated by calculation

Adequacy of study:

key study

Study period:

2014-05-23 to 2014-05-26

Reliability:

2 (reliable with restrictions)

Rationale for reliability incl. deficiencies:

other: Calculation method is used ; calculation method applicable for the endpoint

Qualifier:

equivalent or similar to guideline

Guideline:

OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)

Deviations:

yes

Remarks:

calculation method

Principles of method if other than guideline:

The acute toxicity to daphnia was determined using a validated QSAR for the Mode of Action in question. The first step of the iSafeRat mixture toxicity calculation employs phase equilibrium thermodynamics in order to determine the concentrations of each constituent within the WAF. This fraction equates to the analyzable fraction of a WAF study.
Within the WAF, the constituents also partition between themselves further reducing the bioavailable fraction and thus the toxicity of the mixture compared to the individual constituents. In the calculation the second step is to remove this non-bioavailable fraction.
The final step is to determine the truly bioavailable fraction of the WAF per constituent. The EC50s of each constituent are already known from literature or calculated using the iSafeRat QSAR model. Each value and calculation has been included as a supporting study in the IUCLID. An additivity approach (based on Chemical Activity of each constituent) is used in order to calculate the Effective Loading rate of the WAF.
The method has been validated using data derived from 48-hour EC50 tests on aquatic invertebrates, for which the concentrations of the test item had been determined by chemical analyses over the test period. Further to this the effective loading rate of the WAF is determined by using a series of calculation steps using phase equilibrium thermodynamics and excluding the non-bioavailable fraction.

GLP compliance:

no

Specific details on test material used for the study:

Details on properties of test surrogate or analogue material (migrated information):
not applicable

Analytical monitoring:

no

Details on sampling:

not applicable

Vehicle:

no

Details on test solutions:

not applicable

Test organisms (species):

Daphnia sp.

Details on test organisms:

not applicable

Test type:

other: calculation method

Water media type:

freshwater

Limit test:

no

Total exposure duration:

48 h

Remarks on exposure duration:

48h-EL50 (effective loading rate of WAF)

Post exposure observation period:

not applicable

Hardness:

Hardness is not a necessary component of the WAF calculation

Test temperature:

The Temperature is not a necessary component of the WAF calculation but extremely low or high temperatures could influence the solubility of certain constituents. Therefore, the calculation method is considered acceptable to determine EL50s for daphnia between 12 and 28°C.

pH:

The pH is not a necessary component of the WAF calculation

Dissolved oxygen:

The oxygen concentration is not a necessary component of the WAF calculation

Salinity:

Salinity is not a necessary component of the WAF calculation. However as the fish QSAR for the constituents calculation was based on data from freshwater studies, the resulting calculation is considered valid for freshwater organisms

Nominal and measured concentrations:

The calculation determines measured concentrations

Details on test conditions:

calculation method

Reference substance (positive control):

not required

Duration:

48 h

Dose descriptor:

EL50

Effect conc.:

6.4 mg/L

Conc. based on:

test mat.

Basis for effect:

mobility

Duration:

48 h

Dose descriptor:

EL50

Effect conc.:

2.7 mg/L

Conc. based on:

test mat.

Basis for effect:

mobility

Details on results:

not applicable

Results with reference substance (positive control):

not applicable

Reported statistics and error estimates:

not applicable

Table 1: Expected concentrations at this 48h-EL50 (composition 1: typical composition)

constituents	concentration in the WAF (mg.L-1)
limonene	0.33
α-pinene	0.57
β-pinene	0.11
Δ-3-carene	0.85
camphene	1.40
bornyl acetate	1.66
β-phellandrene	0.15

Table 2: Expected concentrations at this 48h-EL50 (composition 2: theoretical worst case composition)

constituents	concentration in the WAF (mg.L-1)
limonene	0.68
α-pinene	0.54
β-pinene	0.22
Δ-3-carene	0.12
myrcene	0.03
camphene	0.81
bornyl acetate	0.27
β-phellandrene	0.04

Validity criteria fulfilled:

yes

Conclusions:

48h-EL50 for typical composition of Pine needle oil (Pine, Abies siberica, ext.) - Russia = 6.4 mg test item /L and 48h-EL50 for theoretical worst case composition of myrtle oil = 2.7 mg test item/L

Executive summary:

Pine needle oil (Pine,Abies siberica, ext.) – Russia is a Natural Complex Substance (UVCB) with a well-defined composition for which the relative percentage and its reported variation of each constituent is known. Its acute toxicity to aquatic invertebrate property has been investigated using an in-house calculation method that replaces an OECD 202 study and guideline for Testing of Chemicals No. 23 (i.e. WAF conditions). Two compositions have been investigated, the “typical” composition proposed in the SIP and a theoretical worst case composition, derived from data supplied in the SIP that maximizes the concentration of the most toxic constituents.

The first step of the iSafeRat mixture toxicity calculation employs phase equilibrium thermodynamics in order to determine the concentrations of each constituent within the WAF. This fraction equates to the analysable fraction of a WAF study.

Within the WAF, the constituents also partition between themselves further reducing the bioavailable fraction and thus the toxicity of the mixture compared to the individual constituents. In the calculation the second step is to remove this non-bioavailable fraction.

The final step is to determine the truly bioavailable fraction of the WAF per constituent. The EC50s of each constituent are already known from literature or calculated using the iSafeRat QSAR model. Each value and calculation has been included as a supporting study in the IUCLID. An additivity approach (based on Chemical Activity of each constituent) is used in order to calculate the Lethal Loading of the WAF.

The 48-h EL50 was 6.4 mg test material/L for the typical composition ofPine needle oil (Pine,Abies siberica, ext.) – Russia, and the 48-h EL50 was 2.7 mg test material/L for the theoretical worst case composition. EL50 were based on mortality. 

Based on the results of this study,Pine needle oil (Pine,Abies siberica, ext.) – Russia would not be classified as acute 1 to aquatic organisms in accordance with the classification of the CLP.

This toxicity study is acceptable and can be used for that endpoint.

 

Results Synopsis

Test Type: Calculation method

EL50: 6.4 mg test material/L for typical composition

EL50: 2.7 mg test material/L for theoretical worst case composition

Description of key information

Pine needle oil (Pine, Abies siberica, ext.) is a Natural Complex Substance (UVCB) with a well-defined composition for which the relative percentage and its reported variation of each constituent is known. Indeed these variations lead to the identification of two qualities, one named Russia, the other named China. Both qualities were tested to be sure that the worst case composition is clearly taken into account for the endpoint definition. The acute toxicity to aquatic invertebrates property has been investigated using an in-house calculation method that mimics an OECD 202 study and guideline for Testing of Chemicals No. 23 (i.e. WAF conditions) (details are given below. Two theoretical compositions have been investigated for each quality (Russia and China), the “typical” composition proposed by the supplier and a theoretical worst case composition that maximizes the concentration of the most toxic constituents. The 48-h EL50 was 6.4 and 3.6 mg test material/L for the typical composition of Pine needle oil (Pine, Abies siberica, ext.) Russia and China respectively, and the 48-h EL50 was 2.7 mg test material/L for the both theoretical worst case composition. EL50 were based on mortality.Conclusion: The 48-h EL50 for aquatic invertebrates was calculated at 6.4 and 3.6 mg test material/L for the typical composition of Pine needle oil (Pine, Abies siberica, ext.) Russia and China respectively, and the 48-h EL50 was 2.7 mg test material/L for the both theoretical worst case composition.

Key value for chemical safety assessment

Fresh water invertebrates

Fresh water invertebrates

Effect concentration:

2.7 mg/L

Additional information

Pine needle oil (Pine,Abies siberica, ext.) is a Natural Complex Substance (UVCB) with a well-defined composition for which the relative percentage of each constituent is known.Indeed these variations lead to the identification of two qualities, one named Russia, the other named China. Both qualities were tested to be sure that the worst case composition is clearly taken into account for the endpoint definition.

Therefore, it has been decided that the ecotoxicity ofPine needle oil (Pine,Abies siberica, ext.)will be derived from knowledge of the constituents.  The mixture ecotoxicity properties may be derived from the ecotoxicity of the individual constituents using the CLP additivity calculation approach.

 However, it has been observed that CLP additivity calculations for mode of action 1 compounds are unreasonably conservative when compared to classic WAF studies, and this has been proved in a number of cases for natural complex substances. Indeed, natural extract compositions are a mixture of hydrophilic alcohol molecules and hydrophobic terpene molecules. Therefore, when a WAF is performed most of substances fully dissolved in the aqueous phase are the hydrophilic fraction while the hydrophobic fraction (the more toxic elements for MOA 1 substances) may be below their water solubility value. The first step of the iSafeRat mixture toxicity calculation employs phase equilibrium thermodynamics in order to determine the concentrations of each constituent within the WAF. This fraction equates to the analysable fraction of a WAF study. On the other hand the CLP additivity approach is calculated on the basis that all the substances are at their maximum solubility.

Within the WAF, the constituents also partition between themselves further reducing the bioavailable fraction and thus the toxicity of the mixture compared to the individual constituents. In the calculation the second step is to remove this non-bioavailable fraction.

These two reasons explain why ecotoxicity values from WAF studies are always higher for non-polar narcotic mixtures than the calculated values from CLP additivity calculation.

The final step is to determine the truly bioavailable fraction of the WAF per constituent. The EC50s of each constituent are already known from literature or calculated using the iSafeRat QSAR model. Each value and calculation has been included as a supporting study in the IUCLID. An additivity approach (based on Chemical Activity of each constituent) is used in order to calculate the Effective Loading rate of the WAF.

 

 

Using this approach, the48-h EL50 for aquatic invertebrates was calculated at 6.4 and 3.6 mg test material/L for the typical composition of Pine needle oil (Pine,Abies siberica, ext.) Russia and China respectively, and the 48-h EL50 was 2.7 mg test material/L for the both theoretical worst case composition.These EL50 were based on mortality. 

The in-house calculation has been designed to mimic the behaviour of the mixture in a WAF test where the final toxicity is calculated by additivity of the residual bioavailable fraction of each constituent. This approach has been validated using a Natural Complex Substance similar toPine needle oil (Pine,Abies siberica, ext.) (Details on the validations are available in the attached position paper). This calculation is therefore more accurate than the CLP method accurate but remains conservative compared to the experimental value.

 

Based on the results of this study, Pine needle oil (Pine,Abies siberica, ext.) would not be classified as acutely toxic to aquatic organisms in accordance with the classification of the CLP.

This toxicity prediction has been validated and is considered acceptable to fulfil the aquatic invertebrate toxicity endpoint.