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EC number: 248-328-5 | CAS number: 27214-00-2
- 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
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Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- QSAR INFORMATIONS : Quantitative Structure Activity Relationships (QSAR) are theoretical models that can be used to predict in a qualitative or quantitative manner the physico-chemical, toxicological, ecotoxicological and environmental fate properties of compounds from a knowledge of their chemical structure.
1. SOFTWARE : EPI Suite (EPIWEB 4.1)
2. MODEL (incl. version number) : EPIWEB 4.1 ; BIOWIN v4.10 (September 2010)
Principle of method used:
Biodegradability estimates are based upon fragment constants that were developed using multiple linear or non-linear regression analyses, depending on the model:
Biowin1 = linear probability model
Biowin2 = nonlinear probability model
Experimental biodegradation data for Biowin1 and 2 were obtained from Syracuse Research Corporation's (SRC) database of evaluated biodegradation data. This database, and Biowin 1 and 2, are intended to convey a general indication of biodegradability under aerobic conditions, and not for any particular medium.
Biowin3 = expert survey ultimate biodegradation model
Biowin4 = expert survey primary biodegradation model
Biowin3 and 4 yield estimates for the time required to achieve complete ultimate and primary biodegradation in a typical or "evaluative" aquatic environment.
Biowin5 = MITI linear model
Biowin6 = MITI nonlinear model
Biowin5 and 6 are predictive models for assessing a compound’s biodegradability in the Japanese MITI (Ministry of International Trade and Industry) ready biodegradation test; i.e. OECD 301C.
Biowin7 = anaerobic biodegradation model
Biowin7, the anaerobic biodegradation model, is the most recent. As for the other Biowin models, multiple (linear) regression against molecular fragments was used to develop the model, which predicts probability of rapid degradation in the "serum bottle" anaerobic biodegradation screening test. This endpoint is assumed to be predictive of degradation in a typical anaerobic digester.
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL :
OCC(O)COP(O)(O)=O
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
No formal QMRF assessment of the model is currently available, however, the user's guide and the ECHA technical guidance describes all the information.
According to the guidance R.7b - version - June 2017 (page 195) : “The use of QSAR model predictions are of particular relevance and interest when test data are lacking and in addition when assessing multi-constituent substances for which it may often be difficult to find or even to generate test data on relevant individual constituents (including impurities) due to analytical, practical and cost implications.” Furthermore, the Biodegradation Probability Program for Windows (BIOWIN) ) as part of the EPI Suite is recommended in this ECHA Guidance.
- Defined endpoint: Ready biodegradability
- Interpretation: According to the Biowin result file (fixed part), the criteria for prediction are the following:
Biowin1 & 2: ≥ 0.5 --> YES (biodegrades Fast)
Biowin3 & 4: 5.00 -> hours ; 4.00 -> days ; 3.00 -> weeks ; 2.00 -> months ; 1.00 -> longer
Biowin5 & 6: ≥ 0.5 --> YES (readily degradable)
Biowin7: ≥ 0.5 --> YES (biodegrades Fast)
According to the Biowin helpfile, the criteria for an overall YES or NO prediction are as follows:
If Biowin3 (ultimate survey model) ≥ 2.75 AND Biowin5 (MITI linear model) ≥ 0.5, then the prediction is YES (readily biodegradable). If this condition is not satisfied, the prediction is NO (not readily biodegradable)
Cut off point given in the guidance R.7b - version - June 2017 (page 202) were used in a comparison of 177 high production volume (HPV) chemicals in relation to biodegradation test data compared with model predictions by the shown QSAR models (OECD 2004: (ENV/JM/TG/2004)26Rev1). These cut off points are:
BIOWIN1 (linear) & BIOWIN2 (non-linear): 0.5
BIOWIN3: 2.75
BIOWIN5 (linear) & BIOWIN6 (non-linear): 0.5
5. APPLICABILITY DOMAIN
QSAR may be used in estimating the biodegradation of glycerophosphate (as organic ion).
Fragment Coefficients for Biodegradation Models: detailed in QPRF (in the results)
Fragment used and number of instances of fragment:
Aliphatic alcohol [-OH] ; number = 2
-CH2-[linear] ; number = 2
-CH-[linear] ; number = 1
MAX of fragments applicable for Aliphatic alcohol [-OH] (appendix D)
Biowin1 (linear) & Biowin2 (non-linear): 3 -> in the applicability domain (2<3)
Biowin3 (ultimate biodegradation) & Biowin4 (primary biodegradation): 4 -> in applicability domain (2<4)
Biowin5 (MITI linear model) & Biowin6 (MITI nonlinear model): 5 -> in the applicability domain (2<5)
Biowin7: prediction for anaerobic biodegradation -> out of scope for predicting ready biodegradability (not relevant)
-CH2-[linear] ; MAX number for biowin 5 & 6 = 51 -> in the applicability domain
-CH-[linear] ; MAX number for biowin 5 & 6 = 4 -> in the applicability domain
ADEQUACY OF THE RESULT
This endpoint study record should be a Weight of Evidence approach based on several moduls (Biowin 1 to 7). All moduls are used, resulting in a strongness of the weight of evidence. Consequently, this result could be used in a context of key study. - Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- - Software tool(s) used including version: EPI Suite (EPIWEB 4.1)
- Software tool(s) used including version: EPIWEB 4.1 ; BIOWIN v4.10 (September 2010)
- Principle of method used:
Biodegradability estimates are based upon fragment constants that were developed using multiple linear or non-linear regression analyses, depending on the model:
Biowin1 = linear probability model
Biowin2 = nonlinear probability model
Experimental biodegradation data for Biowin1 and 2 were obtained from Syracuse Research Corporation's (SRC) database of evaluated biodegradation data. This database, and Biowin 1 and 2, are intended to convey a general indication of biodegradability under aerobic conditions, and not for any particular medium.
Biowin3 = expert survey ultimate biodegradation model
Biowin4 = expert survey primary biodegradation model
Biowin3 and 4 yield estimates for the time required to achieve complete ultimate and primary biodegradation in a typical or "evaluative" aquatic environment.
Biowin5 = MITI linear model
Biowin6 = MITI nonlinear model
Biowin5 and 6 are predictive models for assessing a compound’s biodegradability in the Japanese MITI (Ministry of International Trade and Industry) ready biodegradation test; i.e. OECD 301C.
- Justification of QSAR prediction: see field 'Justification for type of information' & 'Attached justification' - Specific details on test material used for the study:
- CAS: 27214-00-2
SMILES: [Ca+2].OCC(O)COP([O-])([O-])=O - Remarks on result:
- readily biodegradable based on QSAR/QSPR prediction
- Interpretation of results:
- readily biodegradable
- Conclusions:
- QSAR was made on ready biodegradability for Calcium Glycerophosphate and the result is "YES".
Consequently, according to this result Calcium Glycerophosphate is considered as readily biodegradable.
Reference
Description of key information
QSAR was made on ready biodegradability for Calcium Glycerophosphate and the result is "YES".
Consequently, according to this result Calcium Glycerophosphate is considered as readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- freshwater
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
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