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EC number: 270-485-3 | CAS number: 68442-68-2
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Endpoint summary
Administrative data
Link to relevant study record(s)
- Endpoint:
- basic toxicokinetics, other
- Remarks:
- Expert statement
- Type of information:
- other: Expert statement
- Adequacy of study:
- key study
- Study period:
- 2018-01-26
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: No GLP-conform guideline study, but scientifically valid expert statement based i.a. on studies assessed with Klimisch 1 or 2
- Objective of study:
- absorption
- distribution
- excretion
- metabolism
- toxicokinetics
- Qualifier:
- no guideline required
- Principles of method if other than guideline:
- An extensive assessment of the toxicokinetic behaviour of styrenated diphenylamine was performed, taking into account the chemical structure, the available physico-chemical and toxicological data.
- GLP compliance:
- no
- Radiolabelling:
- other: not applicable
- Species:
- other: not applicable
- Strain:
- other: not applicable
- Details on test animals or test system and environmental conditions:
- not applicable
- Route of administration:
- other: All relevant routes of administration are discussed in the expert statement.
- Vehicle:
- other: not applicable
- Details on exposure:
- not applicable
- Duration and frequency of treatment / exposure:
- not applicable
- Remarks:
- not applicable
- Control animals:
- other: not applicable
- Positive control reference chemical:
- not applicable
- Details on study design:
- not applicable
- Details on dosing and sampling:
- not applicable
- Statistics:
- not applicable
- Type:
- absorption
- Results:
- The relevant absorption rates were estimated to: Oral absorption: approx. 50%, Dermal absorption: approx. 10%, Inhalative absorption: approx. 10%.
- Type:
- distribution
- Results:
- The absolute systemic bioavailablility is rather low and expected to be more extensive in fat tissues than in other tissues.
- Type:
- metabolism
- Results:
- Amine, aromatic and aliphatic hydroxylation were identified as the modes of action during Phase-I-metabolism, and subsequent conjugation is expected.
- Type:
- excretion
- Results:
- Excretion of the parent compound(s) will occur via the GI tract (unabsorbed material) and the bile, and it could be subject to enterohepatic recycling. For metabolites elimination of the Phase 2 conjugated metabolites via the bile is expected.
- Details on absorption:
- Absorption
In general, absorption of a chemical is possible, if the substance crosses biological membranes. In case where no transport mechanisms are involved, this process requires a substance to be soluble, both in lipid and in water, and is also dependent on its molecular weight (substances with molecular weights below 500 are favourable for absorption). Generally, the absorption of chemicals which are surfactants or irritants may be enhanced, because of damage to cell membranes. However, since styrenated diphenylamine was found to be non-irritating to the skin, the possibility of an enhanced absorption due to damaged cell membranes can be excluded.
Due to the lack of experimental absorption data, the following physico-chemical parameters of styrenated diphenylamine will be taken into account when discussing its absorption into the body:
- Molecular weight = 273.38 g/mol, (mono-SDPA), 377.53 g/mol, (di-SDPA) and 481.69 g/mol (tri-SDPA)
- Water solubility = 20.6 µg/L at 20 °C
- Partition Coefficient Log Pow = 4.64 at 22°C and pH 5.2 (experimental data); Log Kow = 5.4482 (mono-SDPA), Log Kow = 7.6051 (di-SDPA), Log Kow = 9.7620 (tri-SDPA) (EpiSuite)
- Vapour pressure = 2.1 x 10E-4 Pa (25 °C)
- Melting point: no melting point between -100 °C and 50 °C, substance is a liquid
- Boiling point: >400°C
Absorption from the gastrointestinal tract
In the small intestine absorption occurs mainly via passive diffusion or lipophilic compounds may form micelles and be taken into the lymphatic system. Additionally, metabolism can occur by gut microflora or by enzymes in the gastrointestinal mucosa. However, the absorption of highly lipophilic substances (Log Pow of 4 or above) may be limited by the inability of such substances to dissolve into gastrointestinal fluids and hence make contact with the mucosal surface. The absorption of such substances will be enhanced if they undergo micellular solubilisation by bile salts. Substances absorbed as micelles enter the circulation via the lymphatic system, bypassing the liver. Consequently, immediate Cytochrome P450 metabolism is less important here as for substances which directly enter the hepatic system via the portal vein.
According to ECHA’s guidance R.7c [ECHA 2008], it is stated that the smaller the molecule the more easily it may be taken up. Molecular weights below 500 are favourable for absorption. With a molecular weight between 273.38 and 481.69 g/mol, absorption is in theory possible, but not highly favoured, especially with increasing numbers of styrene moieties. Mono-substituted isomers are generally more likely to be absorbed than tri-substituted ones. Substances with high Log Pow values, are less favourable for absorption by passive diffusion, which diminishes the ability of styrenated diphenylamine to be absorbed. The experimentally determined logPow of 4.64 is already above the guidance value, the estimated values of the single constituents, i.e. logPow = 5.4482 (mono-SDPA), 7.6051 (di-SDPA), and 9.7620 (tri-SDPA) support the conclusion that the substance is poorly absorbed. Only water-soluble substances will readily dissolve into the gastrointestinal fluids and hence be available for absorption. The substance of interest though has a very low water solubility, i.e. 20.6 µg/L at 20°C. This data indicates that the substance is practically insoluble in water, and so it can be assumed that the solved amount of the substance in e.g. the upper GI tract will be very limited, clearly indicative for a poor absorption. Additionally, the substance is non-toxic, i.e. the available acute 50% lethal doses are above the classification limit of 5000 mg/kg bw, i.e. > 5000 mg/kg bw in rats, no deaths or signs of toxicity occurred, so the actually determined values is an LD0 value of ≥ 5000 mg/kg. Absorption to a certain extent occurred, as in the available OECD 407 study a NOAEL of 100 mg/kg bw/d was determined, but this value is in general not too low, which furthermore indicates either a relative non-toxicity of the substance or its poor absorption.
Styrenated diphenylamine is not biodegradable, so a preliminary metabolism by gut bacteria is less likely, so additional metabolites prior to absorption do also not have to be regarded.
Based on the available data, an absorption rate of 50% or less can be estimated, predominantly due to the insolubility of the substance in water and the high logPow.
Absorption from the respiratory tract
Concerning absorption in the respiratory tract, any gas, vapour or other substances inhaled as respirable dust (i.e. particle size ≤ 15µm) has to be sufficiently lipophilic to cross the alveolar and capillary membranes (moderate Log Pow values between 0-4 are favourable for absorption). The rate of systemic uptake of very hydrophilic gases or vapours may be limited by the rate at which they partition out of the aqueous fluids (mucus) lining the respiratory tract and into the blood. Such substances may be transported out of the lungs with the mucus and swallowed or pass across the respiratory epithelium via aqueous membrane pores. Lipophilic substances (Log Pow >0) have the potential to be absorbed directly across the respiratory tract epithelium. Any lipophilic compound may be taken up by micellular solubilisation but this mechanism may be of particular importance for highly lipophilic compounds (Log Pow >4), particularly those that are poorly soluble in water (1 mg/L or less) that would otherwise be poorly absorbed [ECHA, 2008].
According to the BG Bau [BG Bau, 2017], a vapour pressure of p < 0.01 hPa is very low, p = 1-10 hPa low and p > 10 hPa is high. The 31. BImSchV describes an organic substance as volatile if it has a vapour pressure of 0.01 kPa (i.e. 10 Pa) or more at 293.15 K. Also, according to ECHA’s guidance, substances are not available for inhalation as a gas in a relevant manner with a vapour pressure less than 0.5 kPa (i.e. 500 Pa) (or a boiling point above 150°C) [ECHA, 2008]. With a boiling point of >400°C and a vapour pressure of 2.1 x 10E-4 Pa at 25°, styrenated diphenylamine has a very low vapour pressure and does not need to be regarded a volatile. Hence, the potential inhalation of the substance as a gas is not given and does not need to be regarded. Further, sufficient precautionary measures exclude the formation of droplets of inhalable size or aerosols. In consequence, exposure of humans via inhalation is not likely, so the potential absorption can only be regarded theoretically.
For absorption of deposited material similar criteria as for GI absorption can be applied. In general, either a prolonged exposure due to deposition and subsequent absorption or immediate absorption by micellular solubilisation has to be assumed. The latter mechanism may be of particular importance for highly lipophilic compounds (LogPow >4), particularly those that are poorly soluble in water (1 mg/l or less) and is hence the only relevant here. To be readily soluble in blood, a gas, vapour or dust must be soluble in water and increasing water solubility would increase the amount absorbed per breath. However, the gas, vapour or dust must also be sufficiently lipophilic to cross the alveolar and capillary membranes. Therefore, a moderate log P value (between -1 and 4) would be favourable for absorption. Generally, liquids, solids in solution and water-soluble dusts would readily diffuse/dissolve into the mucus lining the respiratory tract. Hence, with a logPow of 4.64 or even much higher and a virtually non-existing water solubility of 20.6 µg/L, the absorption of this fraction which may not be subjected to ciliary clearance can be considered as very limited by the rate at which the substance partitions out of the fluid in the lung surface. Hence, as due to physical limitations only a very minor portion of the substance may reach the part of the lungs where no clearance mechanisms such a ciliary movements exist and a prolonged high exposure can be excluded, and further, micellular solubilisation is the only reasonable uptake mechanism, the inhalative absorption of the substance can be considered as minor. In theory, if absorption was not limited by physicochemical parameters, a similar absorption rate a via the oral route, i.e. 50%, could be assumed. Due to the physicochemical limitations however, an inhalative absorption of approx. 10% can be assumed as a worst case.
Due to ciliary movements in the upper respiratory tract, the secretion of possibly deposed material with a subsequent swallowing and hence oral exposure after inhalation has to be additionally regarded.
Absorption after dermal exposure
In order to cross the skin, a compound must first penetrate into the stratum corneum and may subsequently reach the epidermis, the dermis and the vascular network. The stratum corneum provides its greatest barrier function against hydrophilic compounds, whereas the epidermis is most resistant to penetration by highly lipophilic compounds. Substances with a molecular weight below 100 are favourable for penetration through the skin and substances above 500 are normally not able to penetrate. The substance must be sufficiently soluble in water to partition from the stratum corneum into the epidermis. Therefore, if the water solubility is below 1 mg/L, dermal uptake is likely to be low. Additionally, Log Pow values between 1 and 4 favour dermal absorption.
Above 4, the rate of penetration may be limited by the rate of transfer between the stratum corneum and the epidermis, but uptake into the stratum corneum will be high. Above 6, the rate of transfer between the stratum corneum and the epidermis will be slow and will limit absorption across the skin. Uptake into the stratum corneum itself may be slow. Moreover vapours of substances with vapour pressures below 100 Pa are likely to be well absorbed and the amount absorbed dermally is most likely more than 10% and less than 100 % of the amount that would be absorbed by inhalation. If the substance is a skin irritant or corrosive, damage to the skin surface may enhance penetration. During the whole absorption process into the skin, the compound can be subject to biotransformation.
In case of styrenated diphenylamine, an evaporation after skin contact does not need to be regarded due to the high boiling point (>400°C) and low vapour pressure, and hence it can be assumed that the substance will remain on the skin until mechanical removal. Furthermore, since the substance is not a skin irritant, additional absorption-enhancing effects can be disregarded, too.
With a molecular weight between 273.38 and 481.69 g/mol in theory absorption via the skin and hence a default dermal absorption rate of 100% [ECHA, 2008] could be assumed.
However, a log Pow of 4.64 or even much higher and a virtually non-existing water solubility of 20.6 µg/L indicate the opposite and are considered to be more important and so, dermal uptake is likely to be low. Therefore, a limited dermal absorption rate can be assumed, most likely about 10%. - Details on distribution in tissues:
- Distribution
In general, it can be stated that the smaller the molecule, the wider is its distribution. A lipophilic molecule (Log Pow >0) is likely to distribute into cells and the intracellular concentration may be higher than extracellular concentration particularly in fatty tissues. It is not possible to foresee protein binding, which can limit the amount of a substance available for distribution. ToxTree modelling [Ideaconsult Ltd, 2004-2013] revealed protein binding alerts, both a Michael acceptor and an alert for nucleophilic aliphatic substitution, but the extent however is unknown. Furthermore, if a substance undergoes extensive first-pass metabolism, predictions made on the basis of the physico-chemical characteristics of the parent substance may not be applicable.
In case of styrenated diphenylamine, no quantitative data is available for distribution patterns. Taking into account its medium molecular weight of between 273.38 and 481.69 g/mol, its lipophilicity and poor water solubility, the absolute systemic bioavailability is rather low and expected to be more extensive in fat tissues than in other tissues, especially when absorption occurred while bypassing the liver.
After oral exposure, the first target will be the gastrointestinal tract, where the substance and possibly bacterial metabolites will be absorbed in small quantities and transferred via the blood stream to the liver. After first pass metabolism, the substance will be further distributed via the bloodstream. Here, especially the kidneys due to their filter function and the heart due to its enormous need for nutrients and consequently large blood flow through coronary arteries will be affected. In general, the estimated metabolites are slightly more hydrophilic due to the hydroxyl groups, which is however expected to be of minor importance given the high lowPow an insolubility in water of the parent compound, influences are considered to be only minor. Since the solubility and hence absorption via the GI tract of the parent compound is rather limited, an excessive formation of metabolites is unlikely and so is a peak exposure to the metabolites. After absorption of the parent compound via other routes, only a subsequent metabolism has to be taken into account, also leading to no relevant peak exposure.
Additionally, accumulation of the parent compound in all directly and indirectly (general supply via bloodstream) involved organs has to be considered. Furthermore, the affection of the lymphatic system via micellar uptake must also be taken into consideration. - Details on excretion:
- Excretion
In general, the major routes of excretion for substances from the systemic circulation are the urine and/or the faeces (via bile and directly from the gastrointestinal mucosa). For non-polar volatile substances and metabolites exhaled air is an important route of excretion. Substances that are excreted favourable in the urine tend to be water-soluble and of low molecular weight (below 300 in the rat) and be ionized at the pH of urine. Most will have been filtered out of the blood by the kidneys though a small amount may enter the urine directly by passive diffusion and there is the potential for reabsorption into the systemic circulation across the tubular epithelium. Substances that are excreted in the bile tend to be amphipathic (containing both polar and nonpolar regions), hydrophobic/strongly polar and have higher molecular weights and pass through the intestines before they are excreted in the faeces and as a result may undergo enterohepatic recycling which will prolong their biological half-life. This is particularly a problem for conjugated molecules that are hydrolysed by gastrointestinal bacteria to form smaller more lipid soluble molecules that can then be reabsorbed from the GI tract. Those substances less likely to recirculate are substances having strong polarity and high molecular weight of their own accord. Other substances excreted in the faeces are those that have diffused out of the systemic circulation into the GIT directly, substances which have been removed from the gastrointestinal mucosa by efflux mechanisms and non-absorbed substances that have been ingested or inhaled and subsequently swallowed. Non-ionized and lipid soluble molecules may be excreted in the saliva (where they may be swallowed again) or in the sweat. Highly lipophilic substances that have penetrated the stratum corneum but not penetrated the viable epidermis may be sloughed off with or without metabolism with skin cells.
For styrenated diphenylamine no data is available regarding its elimination. Concerning the above mentioned behaviour predicted for its metabolic fate, it is unlikely that the parent substance will be excreted unchanged. However, if unchanged excretion is assumed, based on the chemical structure of the constituents of styrenated diphenylamine, its molecular weight and its non-existent water solubility, it is unlikely to be excreted via the urine. The excretion, if any, of the parent compound will occur via the gastrointestinal tract (unabsorbed material) and the bile (small amounts of unchanged compound), and it could be subject to enterohepatic recycling.
Regarding the metabolites of styrenated diphenylamine, an elimination of the Phase 2 conjugated metabolites via the bile is expected. - Metabolites identified:
- yes
- Details on metabolites:
- For details, see attached file. Metabolites of the substance are estimated to be formed via amine, aromatic and aliphatic hydroxylation.
- Conclusions:
- The present expert statement covers all relevant toxicokinetic parameters to assess the behaviour of styrenated diphenylamine in the body, the available information is sufficient to enable one to perform a proper risk assessment. Hence, no further information needs to be gathered and further studies can be omitted due to animal welfare. In conclusion, the substance has a low potential for bioaccumulation in its non-metabolized or metabolized form.
- Executive summary:
In order to assess the toxicokinetic behaviour of styrenated diphenylamine, the available toxicological and physico-chemical data were evaluated.
The substance is expected to be moderately absorbed via the oral route. An oral absorption rate of 50% or less was estimated due to its very low water solubility and high logPow. Due to low vapour pressure of the liquid, the inhalation practically does not have to be regarded, however in theory it has a potential for absorption via respiratory tract epithelium by micellular solubilisation. As a consequence, due to physicochemical limitations, an inhalative absorption rate of 10% can be estimated. Taking into account its poor water solubility, a diminished dermal absorption rate can be assumed, approx. 10%.
So in summary, the absorption rates may be estimated to:
- Absorption via oral route: 50%
- Absorption via inhalative route: 10%
- Absorption via dermal route: 10%
The absolute systemic bioavailablility is rather low and expected to be more extensive in fat tissues than in other tissues. The estimated Cytochrome P450 metabolites of representative structures of the substance are formed via amine, aromatic and aliphatic hydroxylation, and need to be regarded, too, as either a first-pass metabolism or a metabolism by other tissues is expected to occur. The introduction of single hydroxyl groups into the otherwise unchanged molecule, is not expected to alter its ADME behaviour substantially given the magnitude of its logPow and water solubility.
Due to the high logPow and the very low water solubility of styrenated diphenylamine, a certain potential for accumulation in the body is indicated. Nevertheless, a prolonged, extensive accumulation is not expected.
It is unlikely that the parent substance will be excreted unchanged. However, if unchanged excretion is assumed, it is unlikely to be excreted via the urine. The excretion, if any, of the parent compound will occur via the gastrointestinal tract (unabsorbed material) and the bile (small amounts of unchanged compound), and it could be subject to enterohepatic recycling. Regarding the metabolites of styrenated diphenylamine, an elimination of the Phase 2 conjugated metabolites, via the bile is expected.
In conclusion, styrenated diphenylamine has a not very high potential for bioaccumulation, and will be excreted after metabolism.
Reference
See attached expert statement.
Description of key information
Expert statement: Styrenated diphenylamine has a minor potential for bioaccumulation. The relevant absorption rates can be estimated by expert judgement to 50% (oral), 10% (dermal) and 10% (inhalation).
Key value for chemical safety assessment
- Bioaccumulation potential:
- low bioaccumulation potential
- Absorption rate - oral (%):
- 50
- Absorption rate - dermal (%):
- 10
- Absorption rate - inhalation (%):
- 10
Additional information
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.
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