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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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 oral and dermal toxicity, repeated oral dose toxicity study, skin irritation, eye irritation, skin sensitization, in vitro genotoxicity and reproductive toxicity study).

Key value for chemical safety assessment

Absorption rate - oral (%):
50
Absorption rate - dermal (%):
50
Absorption rate - inhalation (%):
100

Additional 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 oral and dermal toxicity, repeated oral dose toxicity study, 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 198.3. It is a liquid and has a water solubility of 10.3 g/L at 20°C and a log Kow of 1.8. 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.


These hypotheses are supported in the 28-day oral study and the screening for developmental and reproductive toxicity study where evidence of liver and kidney changes were observed and indicate absorption from the GI tract and distribution within the body.


The NOAEL was set to 800 mg/kg bw/day in the 28-day repeated dose toxicity study and the screening for developmental and reproductive toxicity 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. Finally, the substance is irritating to the skin which may upon high-dose contact favour dermal penetration of the substance. Nevertheless, no evidence of bioavailability via dermal route was observed in the acute dermal toxicity study up to 2000 mg/kg bw.


 


Respiratory absorption


The potential for inhalation toxicity was not evaluated.


The vapour pressure of the target substance (VP = 0.027 Pa at 20°C) indicated a relatively low volatility and inhalability; therefore, inhalation is not anticipated to be a major contributor to the overall human exposure. Thus, at ambient temperature, relatively low respiratory absorption would be 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 major route of exposure during the normal use(s) of this material.


 


Distribution:


Systemic distribution can be predicted from its physical chemical characteristics. 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:


The results of the 28-day repeated dose toxicity study (OECD 407) and the screening for developmental and reproductive toxicity study (OECD 421) performed in the rat with the substance showed liver changes that are consistent with the increased metabolism associated with detoxification of a xenobiotic:


- dose-related increase in mean absolute and relative liver weights in males and females of all test item-treated groups with statistical significance in animals treated with 800 or 200 mg/kg/day compared to controls animals during the OECD 407 study.


- test substance-related higher mean liver weights in the 400 mg/kg/day group males and in the 800 mg/kg/day group in both sexes during the OECD 421 study.


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 or as metabolites following metabolism.


Any substance that is not absorbed from the gastro-intestinal tract, following oral ingestion, will be excreted in the faeces.


Following dermal exposure, any substance that has penetrated the stratum corneum is likely to be absorbed in the blood following excretion in urine unchanged or as glucuronide and sulfate conjugates if metabolisation in the liver occurs.


 


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.