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Diss Factsheets
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EC number: 812-927-5 | CAS number: 1902936-62-2
- 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
Hydrolysis
Administrative data
- Endpoint:
- hydrolysis
- Type of information:
- other: handbook
- Adequacy of study:
- supporting study
- Study period:
- 1990
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
Data source
Reference
- Reference Type:
- publication
- Title:
- Rate of hydrolysis
- Author:
- Harris JC
- Year:
- 1 990
- Bibliographic source:
- in: Lyman WJ et al., Handbook of chemical property estimation methods, 3rd edition, ACS Washington.
Materials and methods
- Principles of method if other than guideline:
- Hydrolysis is a chemical transformation process in which an organic molecule, RX, reacts with water, forming a new carbon-oxygen bond and cleaving a carbon-X bond in the original molecule. The net reaction is most commonly a direct displacement of X by OH:
R-X + H2O -> R-OH + X- + H+
This process can be distinguished from several other possible reactions between organic chemicals and water such as acid:base reactions, hydration of carbonyls, addition to carbon-carbon bonds, and elimination. Hydrolysis is likely to be the most important reaction of organic compounds with water in aqueous environments and is a significant environmental fate process for many organic chemicals. It is actually not one reaction but a family of reactions involving compound types as diverse as alkyl halides, carboxylic acid esters, organ-ophosphonates, carbamates, epoxides, and nitriles. - GLP compliance:
- no
Test material
- Radiolabelling:
- no
- Remarks:
- not applicable, theoretical evaluation only
Study design
- Analytical monitoring:
- no
- Remarks:
- not applicable, theoretical evaluation only
- Positive controls:
- no
- Negative controls:
- no
Results and discussion
- Transformation products:
- not measured
Dissipation DT50 of parent compound
- Remarks on result:
- not measured/tested
- Remarks:
- not applicable, theoretical evaluation only
Any other information on results incl. tables
Many organic functional groups are relatively or completely inert with respect to hydrolysis. Other functional groups may hydrolyze under environmental conditions.
Table 1. Types of Organic Functional Groups That Are Generally Resistant to Hydrolysis a
Alkanes Alkenes Alkynes Benzenes/byphenyls Polycyclic aromatic hydrocarbons Heterocyclic polycyclic aromatic hydrocarbons Halogenated aromatics/PCBs Dieldrin/aldrin and related halogenated hydrocarbon pesticides |
Aromatic nitro compounds Aromatic amines Alcohols Phenols Glycols Ethers Aldehydes Ketones Carboxylic acids Sulfonic acids |
a. Multifunctional organic compounds in these categories may, of course, be hydrolytically reactive if they contain a hydrolyzable functional group in addition to the alcohol, acid, etc., functionality.
Table 2. Types of Organic Functional Groups That are Potentially Susceptible to Hydrolysis
Alkyl halides Amides Amines Carbamates Carboxylic acid esters Epoxides |
Nitriles Phosphonic acid esters Phosphoric acid esters Sulfonic acid esters Sulfuric acid esters |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- not applicable
- Remarks:
- theoretical evaluation only
- Conclusions:
- Uncertainty in Estimating Values
Hydrolysis rate constants that are estimated by these methods are subject to the following major sources of uncertainty:
(1) The correlation equations are typically based on three to six data points. This reduces confidence in the validity of extrapolating to compounds outside the original data set.
(2) Substituent and reaction constants are obtained from a variety of sources and may refer to temperatures and reaction media that differ from those of the ambient aquatic environment.
(3) Changes in reaction mechanism across a series of related organic compounds is a real possibility.
(4) Correlation equations apply to kH, k0 and kOH individually; it may be impossible to estimate all of the rate constants required for calculation of kT and hence the hydrolysis half-life.
While it is not possible to quantify the probable uncertainties, a qualitative review would suggest that estimated k's be considered order-of-magnitude estimates. If an estimated k is within one or two orders of magnitude of the value considered critical in a given context, a sufficiently reliable value would probably be obtainable only by experimental measurement.
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