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EC number: 250-466-6 | CAS number: 31098-21-2
- 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
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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
- 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 2-Propenoic acid, 2-methyl-,3-sulfopropylester, potassium salt 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
- 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. 100% Dermal absorption: approx. 10% Inhalative absorption: approx. 100%
- Type:
- distribution
- Results:
- Systemic bioavailability of the substance is very high. A high peak exposure can be expected, a very relevant AUC is not to be expected.
- Type:
- metabolism
- Results:
- Epoxydation and Aliphatic hydroxylation were identified as the mode of action during Phase-I-metabolism, and subsequent conjugation is expected.
- Type:
- excretion
- Results:
- SPM and its estimated metabolites are small, charged, hydrophilic and very soluble in water. A very fast excretion of the compounds via the kidneys and urine can be expected. SPM has a minor potential for bioaccumulation, and will be excreted rapidly.
- Details on absorption:
- Absorption
In this chapter, the physico-chemical properties of the substance are used to draw general conclusions for its behaviour and how these properties will influence its oral, inhalatory and dermal absorption. Furthermore, these conclusions will be supported by the available literature data and studies, both on SPM and a read-across substance, SPA.
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 g/mol 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 SPM was found to be non-irritating to the skin and eye, the possibility of an enhanced absorption due to damaged cell membranes can be excluded. This was shown in each a dermal toxicity study, a guinea pig maximisation test on SPA, an OECD 404 skin irritation study, an OECD 405 eye irritation study and is supported by the determination of the pH of SPM (6.4, 40% aqueous solution).
Due to the lack of experimental absorption data, the following physico-chemical parameters of SPM will be taken into account when discussing its absorption into the body:
- Molecular weight = 247.33 g/mol
- Water solubility = 2570 g/L @ 23°C
- Partition Coefficient log Pow = -3.1
- Vapour pressure = 1.05 x 10exp(-9) Pa at 25°C (estimated)
- Melting / Boiling point: The test material changes after start of melting into decomposition at >300°C
- Particle size: Average particle size of the test substance = 24.657µm (D (0.10): 1.82 µm, D (0.50): 9.05 µm, D (0.90): 64.58 µm); ~ 92% are <100 µm (inhalable fraction), ~ 55% are <10 µm (thoracic fraction), ~25% are < 4 µm (respirable fraction)
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 (LogPow 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 g/mol are favourable for absorption. With a molecular weight of 247.33 g/mol, absorption in general can be considered as possible. Also, substances with moderate log P values (between -1 and 4) are favourable for absorption by passive diffusion. The negative log Pow of -3.1 indicates that SPM is more soluble in water than in octanol, i.e. hydrophilic. Water-soluble substances will readily dissolve into the GI fluids. However, absorption of very hydrophilic substances by passive diffusion may be limited by the rate at which the substance partitions out of the GI fluid. The high water solubility of SPM (2570 g/L) and the log Pow value of -3.1 indicates that absorption from the GI tract may be limited. Absorption of rather hydrophilic substances by passive diffusion may be limited by the rate at which the substance partitions out of the gastrointestinal fluid. However, if the molecular weight is low (less than 200) the substance may pass through aqueous pores or be carried through the epithelial barrier by the bulk passage of water. With a molecular weight of 247.33 g/mol, absorption via the bulk passage of water may be slightly hindered, but only to a minor extent.
SPM is inherently biodegradable, a degradation of >99% was reached after 14 days in a inherent biodegradation study. So in general a degradation via gut bacteria can be assumed. However, a noticeable degradation of 6.8% was noted only after 3 days, which is a not relevant timeframe as the passage of the substance through the GI tract can be assumed to occur much faster.
Due to the fact that SPM is inherently biodegradable, a hydrolysis study was not required under REACH. In general, it can be assumed that SPA may undergo chemical changes in the GI tract due to hydrolysis. As a result of the hydrolysis, potassium 3-hydroxypropane-sulfonate and methacrylic acid will be formed as the metabolites. Data indicate a degradation into those products is however minor. Simulation tests in simulated saliva, gastric fluid and intestinal fluid revealed that SPM was stable to 98.5, 98.6, and 99% after 4h at 37°C. Hence, those hydrolysis products also do not have to be considered as their formation is only minor, and absorption estimation may only focus on the parent compound SPM itself. A possible metabolism as described in chapter 3.4 Metabolism does only have to be regarded after absorption already has occurred.
Taking into account the acute and short term oral toxicity data, no relevant further information can be gathered from the acute oral toxicity study and the OECD 422 study on SPA due to the lack of relevant effects noted. In the available OECD 401, no relevant signs of toxicity were observed (LD50 > 5000 mg/kg, LD0 ≥ 5000 mg/kg). No treatment-related adverse effects were noted up to 1000 mg/kg bw/day, the highest dose tested in the available OECD 422 study, only adaptive responses were seen. So it is evident that in general absorption via the GI-tract has occurred. The lack of toxic effects in the other studies is hence less indicative that no absorption has occurred but rather that the substance less hazardous. In the OECD 422 study, in haematology, statistically significant differences observed for MCV, MCH, erythrocytes and reticulocytes in the high dose groups (non-adverse). Also, thymus and spleen weights (absolute and relative) from high dose males were statistically significantly changed. Those effects are strongly indicative for a wide distribution of the test items throughout the body. Hence, a preliminary occurrence of oral absorption of the test item after gavage can reasonably deducted.
So in summary, taking into account the available physico-chemical data of SPM, especially its small molecular weight and high water solubility, its absorption via the GI tract can be considered to be given. This conclusion is supported by minor effects after oral application in an OECD 422 study indicating a distribution of the compounds throughout the body. Due to the lack of further data, an absorption of 100% should be taken into account when performing the subsequent risk assessment, although the actual absorption is possibly less.
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 ≤ 15 µm) has to be sufficiently lipophilic to cross the alveolar and capillary membranes (moderate LogPow 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 (LogPow >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 P >4), particularly those that are poorly soluble in water (1 mg/l or less) that would otherwise be poorly absorbed [ECHA, 2008].
SPM has a very low vapour pressure, 1.05 x 10exp(-9) Pa at 25°C (estimated), and changes after start of melting into decomposition at >300°C, clearly showing that the inhalative absorption as a gas does not have to be regarded.
According to its particle size distribution, the average particle size of the test substance is 24.657µm (D (0.10): 1.82 µm, D (0.50): 9.05 µm, D (0.90): 64.58 µm). Hence, the following distribution is biologically relevant: ~ 92% are <100 µm (inhalable fraction), ~ 55% are <10 µm (thoracic fraction), ~25% are < 4µm (respirable fraction). Those values are taken from the recent version of ECHA’s Guidance document [ECHA, 2015], the former version gave the following information: In humans, particles with aerodynamic diameters below 100 μm have the potential to be inhaled. Particles with aerodynamic diameters below 50 μm may reach the thoracic region and those below 15 μm the alveolar region of the respiratory tract [ECHA, 2008]. As a consequence, there is a rather large fraction potentially reaching the alveolar region of the respiratory tract beyond the bronchi, where no mechanical excretion mechanism as the ciliary movements is available. Although handling of the substance does not lead to a significant exposure due to implemented Risk Management Measures, the potential absorption will 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 not 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 -3.1 and a water solubility of 2570 g/L at 23°C, the absorption of this fraction which may not be subjected to ciliary clearance can be considered as present but may be may be limited by the rate at which the substance partitions out of the fluid in the lung surface.
In summary, taking into account the fraction of SPM being able to reach the lower respiratory tract, its potential to be absorbed and a certain precaution due to the lack of toxicokinetic test data, the inhalative absorption can be estimated to be 100% as a worst case assumption, although the actual absorption is likely to be less.
Absorption after dermal exposure
In general, dry particles will have to dissolve into the surface moisture of the skin before uptake can begin. 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 g/mol 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, logPow 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 SPM, an evaporation after skin contact does not need to be regarded due to the high decomposition temperature 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 neither corrosive nor a skin irritant, additional absorption-enhancing effects can be disregarded, too.
In general, it can be assumed that the substance will be predominantly present in the dissociated and hence charged anion will be present when getting into contact with the moistened skin. The molecular weight of the anion is with 208.23 g/mol rather low, which in general indicates a certain potential to penetrate the skin. However, due to the negative logPow of -3.1, the high water solubility (2570 g/L) and hence hydrophilicity, it is nearly impossible for SPM to penetrate the stratum corneum and to be absorbed via the skin. SPM is not sufficiently lipophilic to cross the lipid rich environment of the stratum corneum and thus dermal uptake will be low [ECHA, 2015]. This is in accordance with the result of the acute dermal toxicity study on SPA, in which no systemic toxicity was found up to 2000 mg/kg bw in male and female rats. However, it should be noted that the skin sensitisation study (GPMT on SPA) showed a positive result, indicating that some dermal absorption takes place
Therefore, a diminished dermal absorption rate can be assumed, most reasonably a resulting maximum dermal penetration of SPM of 10% as a worst case, which is compliant with i.a. the European ECHAs Guidance documents [ECHA, 2008] and scientifically reasonable when e.g. performing route-to-route extrapolations during risk assessment. - 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 (LogPow >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 absolutely foresee protein binding, which can limit the amount of a substance available for distribution. In the case of SPM however, ToxTree modelling gave one protein binding alert, as the substance was identified to contain a Michael acceptor system. The reactivity of that special Michael acceptor system can however not be predicted, as ToxTree modelling identified the same group as a possible DNA binding group, but none of the available genotoxicity tests gave a positive result. However, the positive alert for skin sensitisation was proven by a GPMT on SPA, in which it is very likely that SPA acted as hapten and formed an antigen via protein binding. So it can be assumed that a certain portion of the applied and absorbed amount is not distributed through the entire body but will be retained on the site of impact. 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. However, ToxTree modelling of the CYP450 metabolites indicated that general structure of SPM remains intact and only hydroxylation or epoxidation occurs. The addition of a hydroxyl group could only enhance water solubility, but taking into account the already very high water solubility of 2570 g/l and the low logPow of -3.1, a relevant enhancement of these parameters is not expected. Hence, distribution of the metabolites is expected to follow a similar pattern than the one of the parent compound and no differentiation between the parent compound and metabolites has to be made regarding distribution.
Small water-soluble molecule and ions will diffuse through aqueous channels and pores. The rate at which very hydrophilic molecules diffuse across membranes could limit their distribution. In case of SPM, no quantitative data is available for distribution patterns. Taking into account its rather low molecular weight of 247.33 g/mol, its hydrophilicity and high water solubility, the absolute systemic bioavailability is very high, certainly rather in the aqueous compartment and to a lesser extent in fatty tissues. After oral exposure, the first target will be the gastrointestinal tract, where the substance and possibly bacterial metabolites will be absorbed in high quantities, most likely close to 100% of the ingested amount, and transferred via the blood stream to the liver. After reaching the liver via the portal vein, 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 exposed.
Due to the hydrophilicity, high water solubility and small size, a possible accumulation can be neglected. Since the solubility and hence absorption via the GI tract of the parent compound is rather high, a high peak exposure to the compound(s) and hence high systemic bioavailability can be expected. However, due to their tendency to be excreted rather fast, a very relevant AUC is not to be expected. After the poorer absorption of the parent compound via dermal route, a minor peak exposure has to be considered. The affection of the lymphatic system via micellar uptake however is only of minor importance.
These conclusions are based on the physico-chemical properties of SPM, and which are also applicable for its metabolites, are furthermore supported by the results of the repeated dose OECD 422 study, showing non-adverse effects throughout the body. As so hematological parameters of blood were affected, it is clearly indicated that the substance was distributed in the aqueous compartments of the whole body. As the substance did not show any other toxicologically relevant effects, no further conclusions on its distribution can be drawn.
As a consequence, a wide distribution of the test items throughout the body can be reasonably assumed. Also, due to the nature of the observed effects, secondary effects due to an localized phenomenon, e.g. inflammation of the GI tract without substance uptake, can be excluded. - 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 GI tract 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 SPM no test 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. Nevertheless a similar behaviour regarding excretion can be assumed for the parent compound and most of its degradation products. SPM and its known and estimated degradation products are small, charged and hence hydrophilic and very soluble in water. So a very fast excretion of the compounds via the kidneys and so urine can be expected. Excretion via the GI tract (unabsorbed material) and via the bile and consequent subjection to enterohepatic recycling can be neglected. - Metabolites identified:
- yes
- Details on metabolites:
- For details, see attached file. Metabolites of the substance are estimated to be formed via Epoxydation and Aliphatic hydroxylation.
- Conclusions:
- The present expert statement covers all relevant toxicokinetic parameters to assess the behaviour of 2-Propenoic acid, 2-methyl-,3-sulfopropylester, potassium salt, SPM, 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 no potential for bioaccumulation in its non-metabolized or metabolized form.
- Executive summary:
In order to assess the toxicokinetic behaviour of 2-Propenoic acid, 2-methyl-,3-sulfopropylester, potassium salt (SPM), the available toxicological, ecotoxicological and physico-chemical data were evaluated, also derived from a suitable read-across substance, SPA, as toxicokinetic test data is lacking.
The molecular weight of 247.33 g/mol, a LogPow of -3.1, and a water solubility of 2570 g/L, a high potential for oral absorption is given. The substance is not ready biodegradable and hydrolytically stable, so degradation products do not need to be considered. Taking into account the OECD 422 oral study on SPA, a certain absorption of the test compounds is evident, as changes in haematology can be seen. Hence, a preliminary occurrence of oral absorption of the test item after gavage can reasonably deducted.
SPM has a very low vapour pressure and decomposes during melting, so the inhalative absorption as a gas does not have to be regarded. Based on the distribution of the particle sizes, a relevant fraction reaches the alveolar region of the respiratory tract beyond the bronchi. So either a prolonged exposure due to deposition and subsequent absorption or immediate absorption by micellular solubilisation has to be assumed, and the absorption of the fraction which may not be subjected to ciliary clearance can be considered as rather high.
The substance is neither corrosive nor a skin irritant, additional absorption-enhancing effects can be disregarded. The low molecular weight indicates a certain potential to penetrate the skin, but due to the negative logPow of -3.1, the high water solubility (2570 g/L) and hence hydrophilicity, it is nearly impossible for SPM to penetrate the stratum corneum and to be absorbed via the skin.
So in summary, the absorption rates may be estimated to:
- Absorption via oral route: 100%
- Absorption via inhalative route: 100%
- Absorption via dermal route: 10%
The absolute systemic bioavailability of SPM is very high. Similar distribution patterns can be expected for its metabolites and a possible accumulation can be neglected. A high peak exposure can be expected, but due to their tendency to be excreted rather fast, a very relevant AUC (Area under the curve, i.e. measure for systemic bioavailability) is not to be expected. After the poorer absorption of SPM via the dermal route, a minor peak exposure has to be considered. The sites of the observed non-adverse effects in the OECD 422 study on SPA support a wide distribution of the test item throughout the body.
The negative logPow and the very high water solubility are clearly indicating that for SPM, a rather fast excretion can be expected and the potential of SPM for bioaccumulation in its classic sense is virtually not existing.
Regarding its metabolic fate, Epoxydation and Aliphatic hydroxylation were identified as the mode of action during Phase-I-metabolism. The metabolites formed are not expected to modify essentially the molecular weights, physico-chemical properties and hence ADME behaviour of SPM. It is most likely that the substance of interest will be subject to metabolism by cytochrome P450 enzymes and subsequent conjugation. It is unlikely that SPM will be excreted unchanged. SPM and its estimated metabolites are small, charged and hence hydrophilic and very soluble in water. So a very fast excretion of the compounds via the kidneys and so urine can be expected.
In conclusion, SPM has a minor potential for bioaccumulation, and will be excreted rapidly after metabolism.
Reference
See attached expert statement.
Description of key information
Expert statement: SPM has a minor potential for bioaccumulation. The relevant absorption rates can be estimated by expert judgement to 100% (oral), 10% (dermal) and 100% (inhalation).
Key value for chemical safety assessment
- Bioaccumulation potential:
- low bioaccumulation potential
- Absorption rate - oral (%):
- 100
- Absorption rate - dermal (%):
- 10
- Absorption rate - inhalation (%):
- 100
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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