Registration Dossier
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: 701-124-4 | 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
Additional information
A bioaccumulation study on MDI is waived because exposure to aquatic compartment is unlikely. This is because the rapid hydrolysis of MDI with a t1/2 of 20 hours.
Other data can be considered alongside the fundamental data waiver.
Log Pow for MDI
Degradation products of the hydrolysis
Mesocosm study of MDI
Bioconcentration study on MDI
QSAR modelling
It is recognised that there is a measured log Pow value of 4.51 for monomeric MDI. This log Pow value is of somewhat theoretical as MDI is very unstable in aqueous media (see Section 5.1.2: Hydrolysis). The determination was by an hplc method and comparison to reference chemicals.
MDI reacts with water to form predominantly high molecular weight, inert polyureas and trace amounts of 4,4’-methylenedianiline (MDA). This MDA is considered as the only degradation product of significance, and it has a log Pow value of 1.55. Its measured BCF is < 14 (at 0.2 mg/l) in Cyprinus carpio (EU Risk Assessment Report: 4,4’-methylenedianiline). So, it is concluded that degradation products of MDI do not bioaccumulate.
There is a mesocosm study on PMDI (Heimbach 1993 PMDI dossier 6.1.2a) study, carried out over 112 days, at a loading of 10,000 mg PMDI/l. MDI was detected neither in the water (detection limit 0.005 mg/l) nor in fish (detection limit 0.51 mg/kg). A numeric BCF can not be calculated from these non-detects, but clearly these results show in a practical way that MDI does not accumulate in fish.
A BCF study (III report 11564) carried out according to guideline principles with [14C] radiolabelled 4,4’-MDI and Cyprinus carpio, derives BCF values of 92 and 200 for concentrations of 0.8 and 0.08µg MDI/l. The reported BCF values are highly questionable given the known rapid hydrolysis of MDI under these conditions. Liquid scintillation counting was the method of analysis for all water and fish samples and no analyses of 4,4’-MDI itself were carried out during the course of the study. A BCF value of 200 indicates low potential for bioaccumulation, but it must be recognised that this value probably reflects the bioconcentration of water soluble hydrolysis products which most likely include 4,4’-MDA and low molecular weight ureas. So, again, it is concluded that degradation products of MDI do not bioaccumulate.
Lastly, a BCF value of 439 for 4,4’-MDI may be estimated using the BCFBAFTM (v 3.00) model, a part of the Estimation Program Interface Suite of QSAR tools. An estimated BCF value of 439 for 4,4’-MDI suggests low potential for bioaccumulation.
To summarise, bioaccumulation study is waived due to the unlikely exposure due to rapid hydrolysis of MDI. Supporting data including a mesocosm study, modelling and assessment of degradation products all indicate no potential for significant bioaccumulation.
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.

Route: .live1