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EC number: 909-044-3 | 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
Partition coefficient
Administrative data
Link to relevant study record(s)
- Endpoint:
- partition coefficient
- Type of information:
- (Q)SAR
- Adequacy of study:
- other information
- Study period:
- 18 NOV 2022
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
OECD QSAR toolbox v4.5
2. MODEL (incl. version number)
KOWWIN v1.69
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
multi-constituent substance with 3 constituents
1. COP(O)=O
2. OP(O)=O
3. COP(=O)OC
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
Atom/fragment contribution values, used to estimate the log octanol-water partition coefficient (log P) of organic compounds, have been determined for 130 simple chemical substructures by a multiple linear regression of 1120 compounds with measured log P values. An additional 1231 compounds were used to determine 235 “correction factors” for various substructure orientations. The log P of a compound is estimated by simply summing all atom/fragment contribution values and correction factors occurring in a chemical structure. For the 2351 compound training set, the correlation coefficient (r²) for the estimated vs measured log P values is 0.98 with a standard deviation (SD) of 0.22 and an absolute mean error (ME) of 0.16 log units. This atom fragment contribution (AFC) method was then tested on a separate validation set of 6055 measured log P values that were not used to derive the methodology and yielded an r² of 0.943, an SD of 0.408, and an ME of 0.31. The method is able to predict log P within f 0.8 log units for over 96% of the experimental dataset of 8406 compounds. Because of the simple atom/fragment methodology, “missing fragments” (a problem encountered in other methods) do not occur in the AFC method. Statistically, it is superior to other comprehensive estimation methods.
5. APPLICABILITY DOMAIN
The applicability domain is described by the range of the molecular weight of chemicals in the training set as well as the identification and number of instances of a given fragment in any single compound. Additionally, the applicability domain is extended by inclusion of substructures larger or more complex than "atoms" to improve log P values estimates; hence, correction factors were added to the AFC method. The correction factors are values derived from the differences between the log P estimates from atoms alone and the measured log P values. The correction factors have two main groupings: first, factors involving aromatic ring substituent positions and second, miscellaneous factors. In general, the correction factors are values for various steric interactions, hydrogen-bondings, and effects from polar functional substructures. Individual correction factors were selected through a tedious process of correlating the differences (between log P estimates from atom/fragments alone and measured log P values) with common substructures.
Currently there is no universally accepted definition of model domain. However, users may wish to consider the possibility that log P estimates are less accurate for compounds outside the MW range of the training set compounds, and/or that have more instances of a given fragment than the maximum for all training set compounds. It is also possible that a compound may have a functional group(s) or other structural features not represented in the training set, and for which no fragment coefficient was developed. These points should be taken into consideration when interpreting model results. The predicted substances (methyl hydrogen phosphonate and dimethyl hydrogen phosphate) fall into the MW range of the training set compounds. Thus, it is considered to be in the applicability domain of this model. However, phosphonic acid is an inorganic compound. Inorganic compounds are not included in the training data set for the methodology utilized in this program. Therefore, the predicted substance is outside the estimation domain. - Guideline:
- other: REACH guidance on QSARs Chapter R.6
- Version / remarks:
- May 2008
- Principles of method if other than guideline:
- Software tool(s) used including version: OECD QSAR toolbox v4.5, EPI Suite v4.11
- Model(s) used: KOWWIN v1.69
- Model description:
Atom/Fragment Contribution (AFC (method)
KOWWIN uses a "fragment constant" methodology to predict log Kow. In a "fragment constant" method, a structure is divided into fragments (atom or larger functional groups) and coefficient values of each fragment or group are summed together to yield the log Kow estimate. KOWWIN’s methodology is known as an Atom/Fragment Contribution (AFC) method. Coefficients for individual fragments and groups were derived by multiple regression of 2447 reliably measured log Kow values. Correction factors were developed to be able to consider larger or more complex substructures than the fragments (“atoms”). log Kow = (fini) + (cjnj) + 0.229 (num = 2447, r2= 0.982, std. dev. = 0.217, mean error = 0.159) Where: 1)(fini) is the summation of fi (the coefficient for each atom/fragment) times ni (the number of times the atom/fragment occurs in the structure) 2)(cjnj) is the summation of cj (the coefficient for each correction factor) times nj (the number of times the correction factor occurs (or is applied) in the molecule).
[1]SMILES -- The only data required for KOWWIN to estimate log P is the chemical structure of the compound. The chemical structure is entered into the program as a SMILES notation.
[2]Fragments -- The structure is divided into fragments (atom or larger functional groups).
[3]Correction factors -- The correction factors were derived from a multiple linear regression that correlated differences between the experimental log Kow and the log Kow estimated by the initial equation [log Kow = (fini) + b; where b is the linear equation constant] with the correction factor descriptors.
- Justification of QSAR prediction: see field 'Justification for type of information'. - Type of method:
- calculation method (fragments)
- Partition coefficient type:
- octanol-water
- Specific details on test material used for the study:
- multi-constituent substance with 3 constituents
1. COP(O)=O
2. OP(O)=O
3. COP(=O)OC - Type:
- log Pow
- Partition coefficient:
- >= -1.24 - <= -1.13
- Remarks on result:
- other: No details of temperature and pH
- Conclusions:
- The partition coefficient of the test item has been determined as a range as it is a multi-constituent substance. The partition coefficient of test item is in the range of greater than -1.24 to less than -1.13 by US EPA software KOWWIN v1.69.
- Executive summary:
The partition coefficient of the test item has been determined as a range as it is a multi-constituent substance. The partition coefficient of test item is in the range of greater than -1.24 to less than -1.13 by US EPA software KOWWIN v1.69.
- Endpoint:
- partition coefficient
- Type of information:
- not specified
- Adequacy of study:
- other information
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data from handbook or collection of data
- Principles of method if other than guideline:
- secondary peer reviewed source, valid collection of data
not specified if measured or calculated - GLP compliance:
- not specified
- Partition coefficient type:
- octanol-water
- Type:
- log Pow
- Partition coefficient:
- -1.2
- Endpoint:
- partition coefficient
- Type of information:
- (Q)SAR
- Adequacy of study:
- other information
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other:
- Justification for type of information:
- QSAR prediction
- Principles of method if other than guideline:
- EPI Suite Calculation v 3.20
KOWWIN Program v 1.67 - GLP compliance:
- no
- Partition coefficient type:
- octanol-water
- Type:
- log Pow
- Partition coefficient:
- -1.13
- Executive summary:
The octanol-water partition coefficient of dimethyl phosphonate was calculated with EPI Suite (v3.20):
logPow = -1.13 (Currenta, 2008).
Referenceopen allclose all
methyl hydrogen phosphonate
SMILES : COP(O)=O
CHEM :
MOL FOR: C1 H5 O3 P1
MOL WT : 96.02
-------+-----+--------------------------------------------+---------+--------
TYPE | NUM | LOGKOW FRAGMENT DESCRIPTION | COEFF | VALUE
-------+-----+--------------------------------------------+---------+--------
Frag | 1 | -CH3 [aliphatic carbon] | 0.5473 | 0.5473
Frag | 1 | -O-P [aliphatic attach] |-0.0162 | -0.0162
Frag | 1 | O=P |-2.4239 | -2.4239
Frag | 1 | -OH [phosphorus attach] | 0.4750 | 0.4750
Const | | Equation Constant | | 0.2290
-------+-----+--------------------------------------------+---------+--------
Log Kow = -1.1888
Phosphonic acid
*********************************************************************
* WARNING - The entered structure is an INORGANIC Compound. *
* Very few inorganic compounds were included in the training data *
* set for the methodology utilized in this program. Therefore, *
* inorganic compounds are outside the estimation domain. *
*********************************************************************
-------+-----+--------------------------------------------+---------+--------
TYPE | NUM | LOGKOW FRAGMENT DESCRIPTION | COEFF | VALUE
-------+-----+--------------------------------------------+---------+--------
Frag | 1 | O=P |-2.4239 | -2.4239
Frag | 2 | -OH [phosphorus attach] | 0.4750 | 0.9500
Const | | Equation Constant | | 0.2290
-------+-----+--------------------------------------------+---------+--------
Log Kow = -1.2449
dimethyl hydrogen phosphate
SMILES : COP(=O)OC
CHEM :
MOL FOR: C2 H7 O3 P1
MOL WT : 110.05
-------+-----+--------------------------------------------+---------+--------
TYPE | NUM | LOGKOW FRAGMENT DESCRIPTION | COEFF | VALUE
-------+-----+--------------------------------------------+---------+--------
Frag | 2 | -CH3 [aliphatic carbon] | 0.5473 | 1.0946
Frag | 2 | -O-P [aliphatic attach] |-0.0162 | -0.0324
Frag | 1 | O=P |-2.4239 | -2.4239
Const | | Equation Constant | | 0.2290
-------+-----+--------------------------------------------+---------+--------
Log Kow = -1.1327
no data on temperature or pH value
no data on temperature and pH (calculation method)
TYPE |
NUM |
LOGKOW FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
2 |
-CH3 [aliphaticcarbon] |
0.5473 |
1.0946 |
Frag |
2 |
-O-P [aliphaticattach] |
-0.0162 |
-0.0324 |
Frag |
1 |
O=P |
-2.4239 |
-2.4239 |
Const |
|
EquationConstant |
|
0.2290 |
Log Kow = -1.1327 |
Description of key information
4.7.2 NIOSH, 2009: handbook data; dimethyl phosphonate; logPow: -1.2
4.7.2 KOWWIN, 2008: QSAR calculation; dimethyl phosphonate; logPow: -1.13
EPIWIN(KOWWIN v1.69): QSAR calculation; methyl hydrogen phosphate: -1.19; phosphonic acid: -1.24; dimethyl phosphonate: -1.13
As a key result, vapour pressure of the main constituent was selected.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- -1.19
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.
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