Registration Dossier
Registration Dossier
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: 231-810-4 | CAS number: 7747-35-5
- 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
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
Additional information
To study the absorption, distribution, metabolism, and excretion of CS-1246, rats (four male and female rats per treatment group) were either dosed orally (5 or 200 mg/kg) or dermally (5 mg/kg) with14C-CS-1246 (Saghir et al., 2008). The orally administered CS-1246 biocide was rapidly absorbed (85 to 99%) without any apparent lag time. Absorption via skin was 25-27% of applied dose. Total recovery of radioactivity from the orally dosed rats was 91-109% of the administered dose. Recovery of the dermally applied dose was 66-70%. The lower recovery was considered to be due to volatilization of the test material and/or degradation of parent compound.
The orally absorbed dose was rapidly excreted in urine (83-97%) without any gender difference. Most of the urinary elimination (61-75%) occurred within 12 hours (~43% within 6 hours) of dosing with additional 9-12% during 12-24 hours post-dosing. Total fecal elimination of the dermal dose was only 4% (15-16% of the absorbed dose Elimination of the dermally applied dose was slower with 17-20% of the applied dose being eliminated within 24 hours of dosing.
Only ~1% of the orally administered14C-CS-1246 biocide remained in the tissues after 144 or 168 hours post-dosing. An average of 3% of the dermally dosed14C-CS-1246 remained in the tissues of the animals sacrificed 168 hours post-dosing, most of the remaining radioactivity, (i.e. 2.6 to 2.7%) was found in skin remote from the application site and only 0.8 to 1.7% was recovered from the application site skin. Such a low difference in the residual radioactivity between the dosed site skin and skin at other sites of the body was an indication that complete absorption had been achieved and any additional penetration of radioactivity from the application site was not likely to occur.
In the rats dosed orally with14C-CS-1246, elimination of the radioactivity from plasma was biphasic with most of the elimination occurring during the rapid (a) elimination phase (t½α= 0.1-0.5 hours), with a slower (b) elimination phase (t½b= 4-5 hours). There was some indication of enterohepatic circulation of the biliary eliminated radioactivity between 2-6 hours post-dosing in the low-dose rats, which became pronounced at the high dose. The AUC of radioactivity in plasma at the high dose was 270-281 µg h g-1, which was largely dose proportional; 44-49 fold higher than that observed at the low dose. Consistent with dose proportionally of Cmax, AUC and unsaturated kinetics between the low and high doses, clearance remained unchanged between the two doses.
The absorbed test material was completely metabolized, affording 2-amino-2-ethyl-1,3-propanediol (AEPD) as the only metabolite above 5% of the administered dose in all urine and fecal samples analyzed from all dose groups. Four minor metabolites were also observed above 0.5% of the administered dose, but not identified.
Overall Evaluation of Kinetic and Metabolism Data
In summary, orally administered CS-1246 biocide was rapidly and efficiently absorbed (85 to 99% of applied dose), completely metabolized and readily eliminated from the rat within 144-168 hours after dosing. The dermal dose of CS-1246 was less efficiently absorbed (25 to 27% of applied dose) but as with the orally applied dose the material was completely metabolized and readily eliminated from the body. These data show that accumulation of CS-1246 or any of the metabolites will not occur even with repeat exposures.
References:
Saghir,, Clark, A. J., Beuthin, D.J., McClymont, E. L. and Staley, J. L. (2008)BIOBANÔCS-1246BIOCIDE: Pharmacokinetics and Metabolism in Crl: CD(SD) Rats. The Dow Chemical Company Report No: DR-0365-7827-010 GLP, Unpublished
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.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.