Registration Dossier
Registration Dossier
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EC number: 949-141-8 | CAS number: -
- 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
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC1=CCC(CC1)C(C)(C)O
- Key result
- Type:
- BCF
- Value:
- 67.8 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.83; log Kow used: 3.28)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of l-alpha terpineol was 67.8 L/kg wet-wt (log BCF from regression-based method = 1.83).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of l-alpha terpineol was 67.8 L/kg wet-wt (log BCF from regression-based method = 1.83).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC(C)C1(O)CCC(=CC1)C
- Key result
- Type:
- BCF
- Value:
- 65.8 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.82; log Kow used: 3.26)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of (+)-terpinen-4-ol was 65.8 L/kg wet-wt (log BCF from regression-based method = 1.82).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of (+)-terpinen-4-ol was 65.8 L/kg wet-wt (log BCF from regression-based method = 1.82).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC(C)C1(O)CCC(=CC1)C
- Key result
- Type:
- BCF
- Value:
- 65.8 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.82; log Kow used: 3.26)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of (-)-terpinen-4-ol was 65.8 L/kg wet-wt (log BCF from regression-based method = 1.82).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of (-)-terpinen-4-ol was 65.8 L/kg wet-wt (log BCF from regression-based method = 1.82).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC(C)C1=CCC(C)(O)CC1
- Key result
- Type:
- BCF
- Value:
- 73.3 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.87; log Kow used: 3.33)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of 3-terpinen-1-ol was 73.3 L/kg wet-wt (log BCF from regression-based method = 1.87).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of 3-terpinen-1-ol was 73.3 L/kg wet-wt (log BCF from regression-based method = 1.87).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: C(C(CC1C2)C1(C)C)(=C2)C
- Key result
- Type:
- BCF
- Value:
- 394.9 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 2.597; log Kow used: 4.44)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of alpha pinene was 394.9 L/kg wet-wt (log BCF from regression-based method = 2.597).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of alpha pinene was 394.9 L/kg wet-wt (log BCF from regression-based method = 2.597).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: C(=CC=C(C1)C)(C1)C(C)C
- Key result
- Type:
- BCF
- Value:
- 296 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 2.47; log Kow used: 4.25)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of alpha terpinene was 296 L/kg wet-wt (log BCF from regression-based method = 2.47).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of alpha terpinene was 296 L/kg wet-wt (log BCF from regression-based method = 2.47).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC12CCC(C1)C(C)(C)C2O
- Key result
- Type:
- BCF
- Value:
- 57.4 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.76; log Kow used: 3.17)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of beta fenchol was 57.4 L/kg wet-wt (log BCF from regression-based method = 1.76).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of beta fenchol was 57.4 L/kg wet-wt (log BCF from regression-based method = 1.76).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC(=C)C1CCC(CC1)(O)C
- Key result
- Type:
- BCF
- Value:
- 82.6 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.92; log Kow used: 3.41)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of beta terpineol-cis was 82.6 L/kg wet-wt (log BCF from regression-based method = 1.92).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of beta terpineol-cis was 82.6 L/kg wet-wt (log BCF from regression-based method = 1.92).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC(=C)C1CCC(CC1)(O)C
- Key result
- Type:
- BCF
- Value:
- 82.6 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.92; log Kow used: 3.41)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of beta terpineol-trans was 82.6 L/kg wet-wt (log BCF from regression-based method = 1.92).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of beta terpineol-trans was 82.6 L/kg wet-wt (log BCF from regression-based method = 1.92).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC(C)C12CC1C(C)C=C2
- Key result
- Type:
- BCF
- Value:
- 420.3 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 2.624; log Kow used: 4.48)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of beta thujene was 420.3 L/kg wet-wt (log BCF from regression-based method = 2.624).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of beta thujene was 420.3 L/kg wet-wt (log BCF from regression-based method = 2.624).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC1(C)C2CCC1(C)C(O)C2
- Key result
- Type:
- BCF
- Value:
- 27.7 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.44; log Kow used: 2.69)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of borneol was 27.7 L/kg wet-wt (log BCF from regression-based method = 1.44).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of borneol was 27.7 L/kg wet-wt (log BCF from regression-based method = 1.44).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: C(C(CC1C2)C2)(C1(C)C)=C
- Key result
- Type:
- BCF
- Value:
- 282.7 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 2.451; log Kow used: 4.22)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of camphene was 282.7 L/kg wet-wt (log BCF from regression-based method = 2.451).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of camphene was 282.7 L/kg wet-wt (log BCF from regression-based method = 2.451).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC12CCC(CC1)C(C)(C)O2
- Key result
- Type:
- BCF
- Value:
- 29.8 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.47; log Kow used: 2.74)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of cineole was 29.8 L/kg wet-wt (log BCF from regression-based method = 1.47).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of cineole was 29.8 L/kg wet-wt (log BCF from regression-based method = 1.47).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC1=CCC(CC1)C(C)(C)O
- Key result
- Type:
- BCF
- Value:
- 67.8 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.83; log Kow used: 3.28)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of d-alpha terpineol was 67.8 L/kg wet-wt (log BCF from regression-based method = 1.83).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of d-alpha terpineol was 67.8 L/kg wet-wt (log BCF from regression-based method = 1.83).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: C(=CCC(C(=C)C)C1)(C1)C
- Key result
- Type:
- BCF
- Value:
- 360.5 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 2.557; log Kow used: 4.38)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of d-limonene was 360.5 L/kg wet-wt (log BCF from regression-based method = 2.557).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of d-limonene was 360.5 L/kg wet-wt (log BCF from regression-based method = 2.557).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: COc1ccc(CC=C)cc1
- Key result
- Type:
- BCF
- Value:
- 90.1 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.95; log Kow used: 3.47)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of estragole was 90.1 L/kg wet-wt (log BCF from regression-based method = 1.95).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of estragole was 90.1 L/kg wet-wt (log BCF from regression-based method = 1.95).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC1=CCC(=CC1)C(C)C
- Key result
- Type:
- BCF
- Value:
- 433 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 2.64; log Kow used: 4.50)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of gamma terpinene was 433 L/kg wet-wt (log BCF from regression-based method = 2.64).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of gamma terpinene was 433 L/kg wet-wt (log BCF from regression-based method = 2.64).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC(=C1CCC(C)(O)CC1)C
- Key result
- Type:
- BCF
- Value:
- 89.3 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.95; log Kow used: 3.46)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of gamma terpineol was 89.3 L/kg wet-wt (log BCF from regression-based method = 1.95).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of gamma terpineol was 89.3 L/kg wet-wt (log BCF from regression-based method = 1.95).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC(C)C12CCC(C)(CC1)O2
- Key result
- Type:
- BCF
- Value:
- 42.3 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 1.63; log Kow used: 2.97)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of isocineole was 42.3 L/kg wet-wt (log BCF from regression-based method = 1.63).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of isocineole was 42.3 L/kg wet-wt (log BCF from regression-based method = 1.63).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: C(=CCC(C(=C)C)C1)(C1)C
- Key result
- Type:
- BCF
- Value:
- 360.5 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 2.557; log Kow used: 4.38)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of l-limonene was 360.5 L/kg wet-wt (log BCF from regression-based method = 2.557).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of l-limonene was 360.5 L/kg wet-wt (log BCF from regression-based method = 2.557).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: CC(C)c1ccc(C)cc1
- Key result
- Type:
- BCF
- Value:
- 236 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 2.37; log Kow used: 4.10)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of p-cymene was 236 L/kg wet-wt (log BCF from regression-based method = 2.37).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of p-cymene was 236 L/kg wet-wt (log BCF from regression-based method = 2.37).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: C=C1C(C2)C2(C(C)C)CC1
- Key result
- Type:
- BCF
- Value:
- 576.8 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 2.761; log Kow used: 4.69)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of sabinene was 576.8 L/kg wet-wt (log BCF from regression-based method = 2.761).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of sabinene was 576.8 L/kg wet-wt (log BCF from regression-based method = 2.761).
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- 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
- Remarks:
- Internationally accepted method, EPI Suite, EPA (USA)
- Justification for type of information:
- See attached the QMRF and QPRF for the QSAR model.
- Guideline:
- other: REACH Guidance on QSARs R.6
- Principles of method if other than guideline:
- Meylan, W.M., Howard, P.H, Aronson, D., Printup, H. and S. Gouchie. 1997. "Improved Method for Estimating Bioconcentration Factor (BCF) from Octanol-Water Partition Coefficient", SRC TR-97-006 (2nd Update), July 22, 1997; prepared for: Robert S. Boethling, EPA-OPPT, Washington, DC; Contract No. 68-D5-0012; prepared by: ; Syracuse Research Corp., Environmental Science Center, 6225 Running Ridge Road, North Syracuse, NY 13212.
Meylan, W.M., Howard, P.H., Boethling, R.S. et al. 1999. Improved Method for Estimating Bioconcentration / Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ. Toxicol. Chem. 18(4): 664-672 (1999). - Specific details on test material used for the study:
- SMILES: C(=C(C)C)(CCC(=C1)C)C1
- Key result
- Type:
- BCF
- Value:
- 413.3 L/kg
- Remarks on result:
- other: (Log BCF from regression-based method = 2.616; log Kow used: 4.47)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The BCF of terpinolene was 413.3 L/kg wet-wt (log BCF from regression-based method = 2.616).
- Executive summary:
Using the BCFBAF v3.01 model of EPI Suite v4.11, the BCF of terpinolene was 413.3 L/kg wet-wt (log BCF from regression-based method = 2.616).
Referenceopen allclose all
The BCF of l-alpha terpineol was 67.8 L/kg wet-wt (log BCF from regression-based method = 1.83).
The BCF of (+)-terpinen-4-ol was 65.8 L/kg wet-wt (log BCF from regression-based method = 1.82).
The BCF of (-)-terpinen-4-ol was 65.8 L/kg wet-wt (log BCF from regression-based method = 1.82).
The BCF of 3-terpinen-1-ol was 73.3 L/kg wet-wt (log BCF from regression-based method = 1.87).
The BCF of alpha pinene was 394.9 L/kg wet-wt (log BCF from regression-based method = 2.597).
The BCF of alpha terpinene was 296 L/kg wet-wt (log BCF from regression-based method = 2.47).
The BCF of beta fenchol was 57.4 L/kg wet-wt (log BCF from regression-based method = 1.76).
The BCF of beta terpineol-cis was 82.6 L/kg wet-wt (log BCF from regression-based method = 1.92).
The BCF of beta terpineol-trans was 82.6 L/kg wet-wt (log BCF from regression-based method = 1.92).
The BCF of beta thujene was 420.3 L/kg wet-wt (log BCF from regression-based method = 2.624).
The BCF of borneol was 27.7 L/kg wet-wt (log BCF from regression-based method = 1.44).
The BCF of camphene was 282.7 L/kg wet-wt (log BCF from regression-based method = 2.451).
The BCF of cineole was 29.8 L/kg wet-wt (log BCF from regression-based method = 1.47).
The BCF of d-alpha terpineol was 67.8 L/kg wet-wt (log BCF from regression-based method = 1.83).
The BCF of d-limonene was 360.5 L/kg wet-wt (log BCF from regression-based method = 2.557).
The BCF of estragole was 90.1 L/kg wet-wt (log BCF from regression-based method = 1.95).
The BCF of gamma terpinene was 433 L/kg wet-wt (log BCF from regression-based method = 2.64).
The BCF of gamma terpineol was 89.3 L/kg wet-wt (log BCF from regression-based method = 1.95).
The BCF of isocineole was 42.3 L/kg wet-wt (log BCF from regression-based method = 1.63).
The BCF of l-limonene was 360.5 L/kg wet-wt (log BCF from regression-based method = 2.557).
The BCF of p-cymene was 236 L/kg wet-wt (log BCF from regression-based method = 2.37).
The BCF of sabinene was 576.8 L/kg wet-wt (log BCF from regression-based method = 2.761).
The BCF of terpinolene was 413.3 L/kg wet-wt (log BCF from regression-based method = 2.616).
Description of key information
Weight of evidence: BCFBAF v3.01 model of EPI Suite v4.11. The bioconcentration factor (BCF) was estimated to be in the range of 28 -577 L/kg wet-wt for all main components. The BCF of the test substance has been determined to be the highest of the major components (>1%), i.e. 433 L/kg wet-wt, assuming the worst case scenario.
Key value for chemical safety assessment
- BCF (aquatic species):
- 433 L/kg ww
Additional information
Weight of evidence: The bioconcentration factor (BCF) of the main components are available from EpiSuite calculation:
L-alpha terpineol: EPI-Suite, BCFBAF v3.01. The estimated BCF is 67.8 L/kg wet-wt (log BCF from regression-based method = 1.83)
D-alpha terpineol: EPI-Suite, BCFBAF v3.01. The estimated BCF is 67.8 L/kg wet-wt (log BCF from regression-based method = 1.83)
Terpinolene: EPI-Suite, BCFBAF v3.01. The estimated BCF is 413.3 L/kg wet-wt (log BCF from regression-based method = 2.616).
Gamma terpineol: EPI-Suite, BCFBAF v3.01. The estimated BCF is 89.3 L/kg wet-wt (log BCF from regression-based method = 1.95)
Cineole: EPI-Suite, BCFBAF v3.01. The estimated BCF is 29.8 L/kg wet-wt (log BCF from regression-based method = 1.47)
Isocineole: EPI-Suite, BCFBAF v3.01. The estimated BCF is 42.3 L/kg wet-wt (log BCF from regression-based method = 1.63)
L-Limonene: EPI-Suite, BCFBAF v3.01. The estimated BCF is 360.5 L/kg wet-wt (log BCF from regression-based method = 2.557)
D-Limonene: EPI-Suite, BCFBAF v3.01. The estimated BCF is 360.5 L/kg wet-wt (log BCF from regression-based method = 2.557)
Camphene: EPI-Suite, BCFBAF v3.01. The estimated BCF is 282.7 L/kg wet-wt (log BCF from regression-based method = 2.451)
Alpha terpinene: EPI-Suite, BCFBAF v3.01. The estimated BCF is 296 L/kg wet-wt (log BCF from regression-based method = 2.47)
Gamma terpinene: EPI-Suite, BCFBAF v3.01. The estimated BCF is 433 L/kg wet-wt (log BCF from regression-based method = 2.64)
Alpha pinene: EPI-Suite, BCFBAF v3.01. The estimated BCF is 394.9 L/kg wet-wt (log BCF from regression-based method = 2.597)
3 -terpinen-1 -ol: EPI-Suite, BCFBAF v3.01. The estimated BCF is 73.3 L/kg wet-wt (log BCF from regression-based method = 1.87)
+/-terpinen-4 -ol: EPI-Suite, BCFBAF v3.01. The estimated BCF is 65.8 L/kg wet-wt (log BCF from regression-based method = 1.82)
Beta fenchol: EPI-Suite, BCFBAF v3.01. The estimated BCF is 57.4 L/kg wet-wt (log BCF from regression-based method = 1.76)
cis/trans beta terpineol: EPI-Suite, BCFBAF v3.01. The estimated BCF is 82.6 L/kg wet-wt (log BCF from regression-based method = 1.92)
Beta thujene: EPI-Suite, BCFBAF v3.01. The estimated BCF is 420.3 L/kg wet-wt (log BCF from regression-based method = 2.624)
Sabinene: EPI-Suite, BCFBAF v3.01. The estimated BCF is 576.8 L/kg wet-wt (log BCF from regression-based method = 2.761)
Paracymene: EPI-Suite, BCFBAF v3.01. The estimated BCF is 236 L/kg wet-wt (log BCF from regression-based method = 2.37)
Estragole: EPI-Suite, BCFBAF v3.01. The estimated BCF is 90.1 L/kg wet-wt (log BCF from regression-based method = 1.95)
Borneol: EPI-Suite, BCFBAF v3.01. The estimated BCF is 27.7 L/kg wet-wt (log BCF from regression-based method = 1.44)
Based on the composition of the substance and a weight of evidence approach, the bioconcentration factor (BCF) is determined to be 433 L/kg.
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