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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 246-107-8 | CAS number: 24245-27-0
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- The test item (target substances, CAS 24245-27-0) is the salt of 1,3-diphenylguanidine and mono-hydrochloride. As read-across source substance the uncharged free base of 1,3-diphenylguanidine (CAS 102-06-7) is applied. This is considered appropriate since the target substance is expected to readily dissociate in contact with water such as surface water in the environment or the intestinal fluids or mucosal membranes of an organism. 1,3-diphenylguanidine is considered a weak base. Therefore, it is expected to be present as uncharged molecule at neutral and high pH solutions. However, acidic conditions will lead to protonation of the molecule and the charged ion is expected to be the main present form. Since transformation of the target to the source substance and vice versa is anticipated, kinetics and toxicological behaviour are well transferable from the source to the target substance. This applies for human health endpoints as well as for the aquatic environment.
Moreover, chloride ions are ubiquitously present in every-day nutrition and are part of numerous physiological processes. Therefore, this constituent does not require further assessment in regards to its toxicological behaviour. It is expected to be well regulated by endogenous physiological mechanisms of the organism.
Based on the considerations above, a read-across is considered appropriate and further tests, especially vertebrate studies, are not needed to adequately address this endpoint. Information Requirements are fulfilled according to REACH Annex XI Section 1.5. - Reason / purpose for cross-reference:
- read-across source
- Key result
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 4.2 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Key result
- Duration:
- 96 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 3.2 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
Reference
Description of key information
Based on experimental results obtained with the read-across substance (CAS 102 -06 -7) the LC50 for short-term toxicity with fish is considered to be 4.2 mg/L for the test item.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 4.2 mg/L
Additional information
Read-Across approach
There are no experimental data available regarding acute toxicity to fish with the test item. However, data are available with a structural analogue substance which are suitable and adequate to fulfill this endpoint. For Read-across justification please refer to the respective IUCLID Section.
Short-term toxicity to fish (CAS 102 -06 -7)
The acute toxicity of the read-across substance to fathead minnows (Pimephales promelas) was assessed using the methods outlined by the Committee on Methods for Toxicity Tests with Aquatic Organisms. Water quality parameters of temperature, dissolved oxygen, pH and ammonia were measured throughout the test and were within acceptable limits. As a quality check, the fathead minnows were challenged with areferencecompound, Antimycin A. The observed 96 hour LC50and 95% confidence limits (C.I.) were within the 95% confidence limits reported in the literature (2), indicating that the fish were in good condition. The results of the four day static fish toxicity study using fathead minnows are summarized below.
1,3-diphenylguanidine 96-hour LC50 = 4.2 mg/L (3.2 -5.6 mg/L)
Antimycin A96-hour LC50 = 0.000028 mg/L (0.000023 -0.000034 mg/L)
Also, the results indicated a 96 hour, no observed effect concentration of 1.8 mg/L.
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.