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EC number: 300-226-2 | CAS number: 93924-32-4 A complex combination of hydrocarbons obtained by treatment of Foot's oil with natural or modified clay in either a contacting or percolation process to remove the trace amounts of polar compounds and impurities present. It consists predominantly of branched chain hydrocarbons with carbon numbers predominantly in the range of C20 through C50.
- 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
Link to relevant study record(s)
Description of key information
Short description of key information on bioaccumulation potential result:
Toxicokinetic data for foots oils is being read across from other lubricant base oils because these substances are expected to have similar chemical properties. Toxicokinetics of other lubricant base oils has been examined in rodents. Absorption of other lubricant base oils across the small intestine is related to carbon chain length; hydrocarbons with smaller chain length are more readily absorbed than hydrocarbons with a longer chain length. The majority of an oral dose of mineral hydrocarbon is not absorbed and is excreted unchanged in the faeces. Distribution of mineral hydrocarbons following absorption has been observed in liver, fat, kidney, brain and spleen. Excretion of absorbed mineral hydrocarbons occurs via the faeces and urine. Based on the pharmacokinetic parameters and disposition profiles, the data indicate inherent strain differences in the total systemic exposure (~3 fold greater systemic dose in F344 vs SD rats), rate of metabolism, and hepatic and lymph node retention of C26H52, which may be associated with the different strain sensitivities to the formation of liver granulomas and MLN histiocytosis.
Key value for chemical safety assessment
Additional information
Read across justification
The physical and chemical properties of foots oils are comparable to the other lubricant base oil (OLBO) intermediate streams from which they are derived. Hence their health effects are also similar to those of other lubricant base oils, and the conclusions of the hazard assessment for other lubricant base oils also apply to foots oils. Although other lubricant base oils have not been assessed in toxicokinetic studies, they are similar in composition to highly refined base oils (white oils), so similar toxicokinetic properties would also be expected.
Mineral hydrocarbons (including other lubricant base oils) are chemically inert, and, when ingested, most of the mineral oil (98%) remains unabsorbed in the faeces. Data from studies of “Highly Refined Mineral Oil” (white oil) suggests that small amounts of mineral oil (~2%) are absorbed as such by the animal or human intestinal mucosa and further distributed throughout the body. A very small fraction may undergo further biochemical transformation. Three key read-across studies (Albro 1970, Baldwin 1992, and Ebert 1966) were chosen to assess the toxicokinetic activity of "sufficiently refined" (IP 346 < 3%) OLBOs and "insufficiently refined" (IP 346 ≥ 3%) OLBOs.
"Insufficiently Refined" Other Lubricant Base Oils (IP 346 ≥ 3%)
The test materials in this study, C16 and C18 hydrocarbons, are constituents of other lubricant base oils, and accordingly, the data are expected to be similar to insufficiently refined (IP 346 ≥ 3%) other lubricant base oils in toxicokinetic characteristics.
In a basic toxicokinetic study performed by Baldwin et al., oleum-treated white oil was mixed with the diet of male and female rats in concentrations of 0, 10, 100, 500, 1000, 5000, 10000, and 20000 ppm for a period of 13 weeks. After sacrifice, haematological, clinical chemistry, gross necropsy, tissue residue, and histopathological examinations were preformed. There were no mortalities or adverse effects associated with feeding the rats oleum-treated white oil. Treatment related effects were generally dose-related and more marked in females than in males. After 90 days of treatment moderate multifocal granulomatous changes in mesenteric lymph nodes and liver were observed. Oleum-treated oil caused a greater pathological response then hydrotreated white oil. Oleum-treated white oils are suggested to undergo a process of omega oxidation.
"Sufficiently Refined" Other Lubricant Base Oils (IP 346 <3%)
In a basic toxicokinetic study performed by Baldwin et al., hydrotreated treated white oil was mixed with the diet of male and female rats in concentrations of 0, 10, 100, 500, 1000, 5000, 10000, and 20000 ppm for a period of 13 weeks. After sacrifice, haematological, clinical chemistry, gross necropsy, tissue residue, and histopathological examinations were preformed. There were no mortalities or adverse effects associated with feeding the rats oleum-treated white oil. Treatment related effects were generally dose-related and more marked in females than in males. After 90 days of treatment moderate multifocal granulomatous changes in mesenteric lymph nodes and liver were observed. Oleum-treated oil caused a greater pathological response then hydrotreated white oil. The hydrotreated white oil (applicable to sufficiently refined hydrocarbons, IP 346 < 3%) is metabolized to the corresponding fatty acids of the same carbon chain length as the parent carbons, suggesting omega oxidation.
A toxicokinetics study preformed by Albro et al. evaluated absorption of hydrocarbon mixtures (IP 346 <3%). Simple mixtures of aliphatic hydrocarbons were administered to rats by gastric intubation at dose levels of up to 500 mg/kg b.w. The percentage retention of the aliphatic hydrocarbons was inversely proportional to the number of carbon atoms and ranged from 60% for C14 to 5% for C28 compounds. The major site of absorption was found to be the small intestine.
A toxicokinetics study preformed by Ebert et al. evaluated distribution of tritiated mineral oil (IP 346 <3%) administered orally and via i.p. injections. Male and female rats were dosed with 0.66 mL of radiolabeled mineral oil for thirty-one consecutive days. Radioactivity was measured in extracted tissues after sacrifice. Results indicate that radioactivity is primarily found in liver, fat, kidney, brain, and spleen. Both oral and i.p. routes of administration exhibited the same characteristics of absorption.
A toxicokinetics study preformed by Ebert evaluated excretion of tritiated mineral oil (IP 346 <3%) administered orally and via i.p. injections. Male and female rats were dosed with 0.66 mL of radiolabeled mineral oil for thirty-one consecutive days. Urine and faeces were collected and stored daily for radioactivity analysis. Eighty percent of the tritiated mineral oil administered orally was not absorbed but rather excreted in the faeces two days after treatment. Only 11% of the total dose administered by i.p. injection was excreted in the faeces during the first 8 days of the study. About 8% of the radioactivity administered orally and via intrapeitoneal injection was excreted in the urine during the week following drug administration.
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