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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 700-990-0 | 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
Endpoint summary
Administrative data
Description of key information
90-day oral toxicity study in rat (equivalent or similar to OECD408):
- NOAEL: (M) 107.5 mg/kg bw/day, (F) 124.8 mg/kg bw/day (highest doses tested)
21-day dermal toxicity in rabbit (equivalent or similar to OECD410):
- NOAEL: 10 mg/kg bw/day
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Dose descriptor:
- NOAEL
- 107.5 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
Additional information
In the key study for the oral route, Phosflex 51B was administered to rats in the diet. No treatment related mortality and clinical signs were noted in the animals. The statistically significant differences in hematology and clinical chemistry values and in red blood cell, plasma and brain cholinesterase activities between control and treated animals were minimal, inconsistent and considered not to be of biological significance. A biologically significant increase in liver and adrenal weights (only females) was noted in the high-dose groups, but this was not regarded as a toxic and therefore not an adverse effect. A NOAEL of 107.5 and 124.8 mg/kg bw/day (equivalent to 1600 ppm) was established for males and females, respectively.
Two supporting studies for the oral route were available: a 28-day and a 90-day toxicity study in rats. The subacute toxicity study (equivalent of established a NOAEL of 250 mg/kg bw/day based on liver effects in all dose groups, except for the lowest dose group. The 90-day toxicity study established a NOAEL of 71.6 mg/kg bw/day and 86.2 mg/kg bw/day for male and female, respectively, based on the absence of effects at the highest dose. The key study was chosen as such as it was performed using the most relevant exposure route (oral versus inhalation), a treatment period of 90 days (as compared to 28-days in the supporting study with a higher NOAEL) and it tested the highest concentration at which no adverse effects were observed (as compared to the other 90-day oral toxicity study).
Two subacute repeated dose toxicity studies for the dermal route are available. In the key study, rabbits were exposed to tBuTPP for 21 days. An evident dose response depression of terminal cholinesterase was observed in the treated males and females, which was significant in the mid and high dose, a NOAEL of 10 mg/kg bw/day was derived. This finding was supported by a second 21 -day study in rabbits, in which a LOAEL of 100 mg/kg bw/day was observed based on the same effects. As in the 90 -day oral repeated dose toxicity study, significant effects on cholinesterase were noted at the interim measurement after 45 days of exposure, but these effects were minimal and considered not to be of biological significance after the end of treatment (90 days), the NOAEL from this study was used as key value for derivation of the DNEL.
Additionally a 90-day inhalation toxicity study in rats was available that established a NOAEL of 101.1 mg/m3 based on the absence of effects at this dose (highest tested). As no effects were observed at the highest dose, it was decided to use the NOAEL from the oral 90 -day study as key value for derivation of the DNEL.
Justification for classification or non-classification
The most critical NOAEL established for t-BuTPP was 107.5 mg/kg bw/day. When considering the guidance values for classification as outlined in Annex I of 1272/2008/EC (significant effect observed at 100 mg/kg bw/day) and Annex VI of 67/548/EEC (significant effect observed at 50 mg/kg bw/day), the substance does not need to be classified for repeated dose toxicity.
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.