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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Administrative data

Link to relevant study record(s)

Description of key information

No specific toxicokinetic studies are required at this tonnage band but a toxicokinetic assessment was made based on the results of the toxicity studies (acute and repeated oral dose toxicity studies, skin irritation, eye irritation, skin sensitization, in vitro genotoxicity and reproductive toxicity study).

Key value for chemical safety assessment

Bioaccumulation potential:
no bioaccumulation potential
Absorption rate - oral (%):
50
Absorption rate - dermal (%):
50
Absorption rate - inhalation (%):
100

Additional information

No specific studies on the absorption, distribution, metabolism and elimination (ADME) of the substance are available and/or required at this tonnage band. Moreover, the very low toxicity of Rhubafuran suggests that it may be considered inappropriate at this time to conduct further animal work to support ADME.


A toxicokinetic assessment was made based on the results of the toxicity studies (acute and repeated oral dose toxicity studies, skin irritation, eye irritation, skin sensitization, in vitro genotoxicity and reproductive toxicity study).


 


 


The notified substance is a small organic molecule with a molecular weight of 176.59. It is a liquid and has a water solubility of 650 mg/L at 20°C and a log Kow of 3. The physico-chemical properties of the test item would suggest the substance is likely to be absorbed via dermal, inhalation and gastric routes following exposure.


 


Absorption:


Oral/GI absorption


The physical chemical characteristics described above suggest that the target substance is of adequate molecular size (< 500 g/mol) to participate in endogenous absorption mechanisms within the mammalian gastrointestinal tract. The target substance is likely expected to cross gastrointestinal epithelial barriers. The absorption may be potentiated by the ability of the substance to dissolve into gastro-intestinal fluids and hence make contact with the mucosal surface. N-octanol/water partition coefficient and molecular weight are in ranges which favour oral absorption by passive diffusion.


These hypotheses are supported in the Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test (OECD 422) where evidence of liver and kidney changes were observed and indicate absorption from the GI tract and distribution within the body.


The lowest NOAEL was set to 200 mg/kg bw/day in this study.


 


Dermal absorption


The uptake of the substance into the stratum corneum is enhanced considering its potential to solubilize lipids allowing the transfer between the stratum corneum and the epidermis. Furthermore, it is assumed that the dermal uptake of the substance in the blood is increased by its high water solubility. 


 


Respiratory absorption


The potential for inhalation toxicity was not evaluated.


The vapour pressure of the target substance (VP = 2.5 Pa at 20°C) indicated a low volatility and inhalability and therefore no exposure by inhalation is anticipated. Thus, at ambient temperature, no respiratory absorption is expected under normal use and handling of the substance.


Based on the result of the physico-chemical properties, toxicological properties and pattern of use, e.g. potential human exposure, it has been determined that inhalation is not anticipated to be a potential route of exposure during the normal use(s) of this material.


 


Distribution:


Systemic distribution can be predicted from its physical chemical characteristics. As a small molecule a wide distribution is expected. Considering that the substance is highly water soluble, it is suggested that, upon systemic absorption by oral and dermal routes or by inhalation, the substance may be transported through the circulatory system in association with a carrier molecule. Afterwards, based on its character, the substance may cross cellular barriers without potential to accumulate into fatty tissues.


 


Metabolism:


As a small molecule a wide distribution is expected. The results of Combined Repeated Dose Toxicity Study with the Reproduction/Developmental Toxicity Screening Test (OECD 422) performed in the rat with the substance showed liver changes that are consistent with the increased metabolism associated with detoxification of a xenobiotic. This liver induction confirmed that a non-negligible part of the substance is metabolised following gastrointestinal tract absorption.


 


Excretion:


The substance, having a molecular weight lower than 500 g/mol, is expected to be mainly excreted in urine unchanged or as glucuronide and sulfate conjugates following oral exposure and inhalation. A minor amount (< 10%) may be excreted in bile as such or as metabolites following metabolism. Moreover, the n-Octanol/water partition coefficient is suggestive of accumulation of unchanged test item in fatty tissues subsequent to absorption from gastrointestinal tract or from lungs. Any substance that is not absorbed from the gastro-intestinal tract, following oral ingestion, will be excreted in the faeces.


 


No other indications on the toxicokinetic behaviour could be derived from the results of the available studies and no specific studies on the absorption, distribution, metabolism and excretion are available.