Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 298-577-9 | CAS number: 93819-94-4
- 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
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was performed according to guideline with analytical monitoring by a substance specific method.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Deviations:
- no
- GLP compliance:
- yes
- Remarks:
- This study was not performed by a GLP certified laboratory. Hydrolysis was considered to be a phsyico-chemical endpoint, therefore, not conducting the study to GLP was considered acceptable.
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- - Sampling intervals for the parent/transformation products: Samples were evaluated for depletion of the parent compound (dialkyldithiophosphate) by 31P-NMR (phosphorus-Nuclear Magnetic Resonance) spectroscopy once at the end of the 5 day Tier 1 preliminary test
-Sampling methods for the volatile compounds, if any: no volatile components
- Sampling intervals/times for pH measurements: pH was measured at the start and at the end of the 5 day test period with a Beckmann Model 360 meter calibrated prior to use.
- Sample storage conditions before analysis: Samples were freshly prepared for the 5 day Tier 1 study. Samples were immediately analyzed for hydrolysis products after the 5 day incubation period at 50 degrees C.
- Other observation, if any (e.g. precipitation, color change etc.): At pH 4 and 7, mixtures of the test material in buffer were cloudy. A sediment of white solids was observed at pH 9. A slight oil slick was observed at all pHs. These observations were expected as the test substance is a mixture of oil and Zn metal complexes with organic ligands of variable water solubility. At the end of the 5 day test period, mixtures were centrifuged at 2100 rpm for 30 min. resulting in a clear aqueous phase on which NMR testing was performed. - Buffers:
- - pH 4
- Type and final molarity of buffer: 0.1M potassium biphthalate + 0.1N NaOH
- Composition of buffer: 0.4 mL of 0.1NaOH + 50 mL biphthalate/100 mL distilled, deionized water (as described in OECD 111)
pH 7
- Type and final molarity of buffer: 0.2M Tris-maleate buffer
- Composition of buffer: Stock solution: 24.2 g Tris(hydroxymethyl)aminomethane + 23.2 g maleic acid / 1000 mL. 50 mL of stock was adjusted to pH 7 with 0.1M NaOH and diluted to 100 mL with distilled, deionized water.
pH: 9
- Type: Sodium borate buffer
-Composition: (Purchased) Supplier: EMD chemicals Catalog Number EM-BX1658-1
-Description: pH value 9.0 colorless, solution accurate to +/- 0.01 pH units at 25 deg. C. Standardized against solutions whose certification is NIST traceable. - Details on test conditions:
- TEST MEDIUM
-0.5 g of test material were weighed directly into three separate test flasks
-500 mL of one of the following buffers was added (one to each flask): pH 4 phthalate, pH 7 tris/maleate, pH 9 borate buffer
-pH 4 and pH7 buffers were freshly prepared in distilled, deionized water; pH 9 buffer was purchased
TEST SYSTEM
- Type, material and volume of test flasks, other equipment used: test flasks consisted of acid washed and dried 1000 mL glass flasks fitted with a gas inlet adaptor, thermowell, reflux condenser and a mechanical stirrer.
- Measures taken to avoid photolytic effects: test flasks were wrapped with aluminum foil to eliminate light
- Measures to exclude oxygen: the mixtures were heated to 50 deg. C under a stream of nitrogen at 0.1 cfh to minimize oxidation. The nitrogen sweep was discontinued ater the mixtures reached 50 deg. C to prevent evaporation.
-Temperature: Mixtures were maintained at 50 deg. C for the 5 day test period and monitored regularly by thermometer. - Duration:
- 5 d
- pH:
- 4
- Temp.:
- 50 °C
- Initial conc. measured:
- 1 000 mg/L
- Duration:
- 5 d
- pH:
- 7
- Temp.:
- 50 °C
- Initial conc. measured:
- 1 000 mg/L
- Duration:
- 5 d
- pH:
- 9
- Temp.:
- 50 °C
- Initial conc. measured:
- 1 000 mg/L
- Number of replicates:
- no replicates
- Positive controls:
- no
- Negative controls:
- no
- Statistical methods:
- n/a
- Preliminary study:
- In the 5-day Tier 1 preliminary study, 93.4% of the parent compound was recovered at pH 7. At pH 4 and 9, the recovery was 100%.
At pH 9, the zinc metal of the parent complex was exchanged for the sodium of the buffer forming a sodium dialkyldithiophosphate product and an insoluble sediment of zinc oxide/hydroxide. The 31P-NMR spectrum showed a single peak at 108 ppm indicating the alkyldithiophosphate ligands remained intact after the metal exchange. The sodium dialkyldithiophosphate product was confirmed by ICP analysis which showed 0% zinc and the presence of sodium in the test mixture after the 5-day study which was not present in the starting mixture.
A < 10% change in the concentration of the dialkyldithiophosphate ligands of the parent compound at pH 4, 7 and 9 meets the OECD 111 criterion for a hydrolytically stable material. A full hydrolysis study is not required. - Test performance:
- The pH and temperature were maintained throughout the 5-day study. There were no unexpected occurrences that would have affected the test results. Test mixtures were cloudy and an slight oil slick was observed at all pHs. At pH 9, the zinc metal of the parent complex precipitated as zinc oxide. These observations were expected as the test substance contains a mixture of oil and zinc metal complexes with organic ligands of different water solubilities. All analyses were performed on the clear supernants
- Transformation products:
- no
- % Recovery:
- 100
- pH:
- 4
- Temp.:
- 50 °C
- Duration:
- 5 d
- % Recovery:
- 93.4
- pH:
- 7
- Temp.:
- 50 °C
- Duration:
- 5 d
- % Recovery:
- 100
- pH:
- 9
- Temp.:
- 50 °C
- Duration:
- 5 d
- Remarks on result:
- hydrolytically stable based on preliminary test
- Validity criteria fulfilled:
- not specified
- Conclusions:
- Under the conditions used in this study, hydrolytic degradation of the dialkyldithiophosphate (DDP) anion never exceeded 10%, even with fully saturated solutions. However, the zinc complex of the DDP anion was found to be labile in aqueous solution and it was not possible to definitively determine the cation associated with the DDP anion in solution when multiple cations were present.
- Executive summary:
A Tier 1 preliminary hydrolysis study was performed according the OECD 111 guideline, Annex 1, tiered hydrolysis scheme. Mixtures of the test substance were prepared in buffers at pH 4, 7 and 9 and maintained at 50 degrees C for 5 days. Following the 5 day incubation, mixtures were evaluated by 31P-NMR (phosphorus-Nuclear Magnetic Resonance) spectroscopy for depletion of the alkyldithiophosphate signals between 112 - 108 ppm and the appearance of other peaks which could be identified as hydrolysis products.
At pH 4, 7 and 9, the 31P-NMR spectra showed a change of < 10% in the concentration of the alkyldithiophosphate ligands bound to the zinc metal indicating the substance meets the OECD 111 criterion for a hydrolytically stable material.
At pH 9, the zinc metal was exchanged for the sodium of the buffer forming a sodium salt with the alkyldithiophosphate ligands remaining intact. In the exchange, the zinc metal was precipitated as insoluble zinc oxide/hydroxide. No other peaks besides the alkyldithiophosphates (between 112 – 108 ppm) were detected in the NMR spectrum.
Based on the results of the 5-day Tier 1 preliminary test, the substance was determined to be hydrolytically stable and a full study is not required.
Under the conditions used in this study, hydrolytic degradation of the dialkyldithiophosphate (DDP) anion never exceeded 10%, even with fully saturated solutions. However, the zinc complex of the DDP anion was found to be labile in aqueous solution and it was not possible to definitively determine the cation associated with the DDP anion in solution when multiple cations were present.
Reference
Table 1. Results of 5 -day Preliminary Hydrolysis Test (at 50 0C)
pH |
4 |
7 |
9 |
Buffer System |
phthalate |
tris/maleate |
borate |
Approx. saturation concentration (ppm) |
2700 |
2700 |
2700 |
Starting Concentation (ppm) |
1000 |
1000 |
1000 |
% recovery after 5 days |
100 |
93.4 |
100 (1) |
(1) 100% recovery of dialkyldithiophosphate with an exchange of zinc in the parent compound for the sodium of the pH 9 buffer occurred.
Description of key information
Under the conditions used in this study, hydrolytic degradation of the dialkyldithiophosphate (DDP) anion never exceeded 10%, even with fully saturated solutions. However, the zinc complex of the DDP anion was found to be labile in aqueous solution and it was not possible to definitively determine the cation associated with the DDP anion in solution when multiple cations were present.
Key value for chemical safety assessment
Additional information
Read-across from other, structurally closely related ZDDPs is justified because of structural similarity and analogy of properties and effects. see section 13 for justification 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.