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EC number: 809-920-4 | CAS number: 1047637-37-5
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 13 Augst 2007 - 29 January 2008
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 008
- Report date:
- 2008
Materials and methods
- Objective of study:
- absorption
- distribution
- excretion
- metabolism
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 417 (Toxicokinetics)
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 2,2-bis(chloromethyl)trimethylene bis(bis(2-chloroethyl)phosphate)
- EC Number:
- 253-760-2
- EC Name:
- 2,2-bis(chloromethyl)trimethylene bis(bis(2-chloroethyl)phosphate)
- Cas Number:
- 38051-10-4
- Molecular formula:
- C13H24Cl6O8P2
- IUPAC Name:
- 2,2-bis(chloromethyl)propane-1,3-diyl tetrakis(2-chloroethyl) bis(phosphate)
- Details on test material:
- NON-RADIOLABELLED
Product name: TL 10 ST
Supplier: Albemarle
RADIOLABELLED
Position radiolabel: chloroethyl-14C(U)
Specific activity: 24.3 mCi/mmol
Supplier: Moravek
Constituent 1
- Radiolabelling:
- yes
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Germany
- Age at study initiation: 9 - 10 weeks
- Weight variation at study initiation: did not exceed +/-20% of average weight
- Fasting period before study:
- Housing: in groups of 4-5 during acclimatisation, individually during study
- Individual metabolism cages: yes
- Diet: ad libitum (commercial rat diet)
- Water: ad libitum
- Acclimation period: at least 5 days
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 - 25
- Humidity (%): 40 - 70
- Air changes (per hr): about 10
- Photoperiod (hrs dark / hrs light): 12h/12h
Administration / exposure
- Route of administration:
- other: oral and intravenous
- Vehicle:
- other: oral: 0.5% hydroxypropyl-methyl cellulose in water; i.v. Cremophor ELP/ethanol 49.7: 50.3 (v/v)
- Details on exposure:
- DOSE PREPARATION
- Oral: test substance in 0.5% hydroxyproyl-methylcellulose in water, prepared freshly on day before dosing
- Intravenous: test substance mixed with 430 microL of Cremophor ELP/ethanol (49.7:50.3 v/v) and diluted with saline to 10 mL just before dosing
- Dose formulation consisted of radiolabelled material diluted with non-radiolabelled test substance to required concentrations - Duration and frequency of treatment / exposure:
- single oral (group A+B) or intravenous (group C) dose
Doses / concentrations
- Remarks:
- Doses / Concentrations:
- Group A: 15 mg test substance/kg bw - oral
- Group B: 600 mg test substance/kg bw - oral
- Group C: 15 mg test substance/kg bw - intravenous
- No. of animals per sex per dose / concentration:
- 4 male and 4 female animals/group
- Control animals:
- no
- Details on dosing and sampling:
- PHARMACOKINETIC STUDY
- Tissues and body fluids sampled: urine, faeces, blood kinetics, tissues, carcass (same for all 3 groups, except tissues only for group A+B) expired air (CO2 and volatiles) was collected at 24 h intervals for 48 h.
- Time and frequency of sampling: blood (100 microL) at 30 min, 1h, 2h, 3h, 4h, 6h, 8h, 24h, 48h, 96h after dosing and at sacrifice (7 days); urine and feaces collected daily; expired air sampled on day 1 and 2 after dosing
METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: urine (in selected samples to cover > 90% of excreted dose)
- Time and frequency of sampling: twice, 0-24h and 24-48h after dosing
- From how many animals: pooled by group, sex and time point
- Method types for identification HPLC, Liquid scintillation counting, LC-MS/MS - Statistics:
- Pharmacokinetic parameters calculated by EXcel program developed by TNO (2-compartment model for intravenous dose and 1-compartment model for oral dose)
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- Following oral administration of [14C]-2,2-bis(chloromethyl) trimethylene bis(bis(2-chloroethyl) phosphate), highest concentrations of radioactivity in the blood were found at 8 hours post dosing in both sexes and both concentrations. The Cmax values for males and females of the low dose were comparable (1.73 and 1.5 µg/g, respectively), but were higher for females in the high dose (18.9 and 29.5 µg/g, for males and females respectively). The bioavailability derived from the area under the curve after oral dosing in comparison with that after i.v. dosing was 142 and 143% for males and females of the high dose group respectively and 47 and 55% for males and females of the low dose group respectively.
In the oral low dose and IV dose groups, the AUC0-168hr and AUC0-infinity values were comparable for males and females. However, in the oral high dose group, the AUC values were higher in females than males. The higher AUC values following the oral dose when compared with the IV dose are probably due to differences in metabolism, since the elimination half-lives for the two routes are comparable. The greater than 100% bioavailability seen is due to the slightly lower AUC0-infinity values observed for IV dose when compared with the oral dose (approximately 114 and 168 µg/g/hr, respectively). iIt should be noted that in calculating the bioavailability in the high dose, the reference IV AUC was taken from a lower dose IV administration. Also, after oral high dose administration only very little radioactivity attributable to the intact parent compound was found in the faeces (<1%) indicating practically complete absorption from the gastro-intestinal tract.
Total retention of radioactivity was around 2.5% after oral low dose and about 0.8% after high oral dose - Details on distribution in tissues:
- The total recovered radioactivity was around 80%, regardless of the dose, route of administration or sex. Following oral dosing, the total retention of radioactivity was around 2.5% after the low dose and 0.8% after the high dose, with most of the radioactivity excreted within 3 days.
At 168 hours post dose, the highest concentrations of radioactivity were found in the liver, kidney, adrenals and abdominal skin in both sexes, and in uterus of both low and high dose females. The lowest radioactivity was found in brain, plasma and fat, the latter indicating no bioaccumulation of the test substance. Therefore, [14C]-2,2-bis(chloromethyl) trimethylene bis(bis(2-chloroethyl) phosphate), or its metabolites, was distributed all over the body, but no specific target organs, other than the organs of elimination, were identified.
- Distribution in tissues irrespective of dose administered (group A+B, oral dosing)
- Highest concentration of radioactivity found in liver, kidney, adrenals and abdominal skin
- Lowest concentration of radioactivity found in brain, plasma and fat
- Details on excretion:
- Excretion occurred mainly by the biliary route (approx. 60%), with excretion in urine approximately 20% and a small amount of radioactivity exhaled as 14CO2. Volatile radioactivity could not be detected; however the study report states that it is possible that part of the radioactivity was exhaled as ethylchloride or more likely 2-chloroethanol, as all major metabolites were missing an ethylchloride group. These compounds are very volatile and could not be trapped in the conditions of the experimental design. The study director also comments in the study report that this could explain the low recovery of total radioactivity (of 80%) since one ethylchloride group attributes 25% of the radioactivity of the molecule.
Total recovered excreted radioactivity was around 80% independently of dose route and sex
Toxicokinetic parametersopen allclose all
- Test no.:
- #1
- Toxicokinetic parameters:
- Cmax: 1.50-1.73 microg/g at 8h - oral, low dose
- Test no.:
- #2
- Toxicokinetic parameters:
- Cmax: 18.9-29.5 microg/g at 8h - oral, high dose
- Test no.:
- #3
- Toxicokinetic parameters:
- Cmax: 5.07-5.25 mircog/g at 0h - intravenous, low dose
- Toxicokinetic parameters:
- Tmax: oral all doses: 8 h
- Toxicokinetic parameters:
- half-life 1st: 102-111 h -elimination oral
- Toxicokinetic parameters:
- half-life 1st: 99-113h - elimination, intravenous
- Toxicokinetic parameters:
- AUC: 0-168 h low dose (m+f): 115.4 microg/g h
- Toxicokinetic parameters:
- AUC: 0-168 h high dose m: 1450 f: 1822 microg/g h
- Toxicokinetic parameters:
- AUC: 0-168 h i.v. (m+f) 81.3 microg/g h
- Toxicokinetic parameters:
- AUC: 0-infinity oral low dose m: 166.9, f: 168.3 microg/g h
- Toxicokinetic parameters:
- AUC: 0-infinity oral high dose: m: 2177, f: 2632 microg/g h
- Toxicokinetic parameters:
- AUC: 0-infinity i.v.: m: 113.9, f: 115.4 microg/g h
- Toxicokinetic parameters:
- other: Bioavailability: 142% - oral, low dose (male+female)
- Toxicokinetic parameters:
- other: Bioavailability: 47% (male), 55% (female) - oral high dose
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- - Small amount of intact radiolabelled test substance detected in feaces (<1%), only first 2 days, indicating almost complete absorption from gastro-intestinal tract
- At least 12 metabolites detected in urine, at least 14 in feaces
- 4 major metabolites (more than 5% of administered dose (4 in feaces, 1 also in urine)
- Metabolite 1: present up to 30% of administered dose (all groups), C11H22O8Cl5P2
- Metabolite 2: present up to 20% of administered dose (lower in low oral dose group), C13H24O10Cl5P2
- Metabolite 3 + 4: present up to 9% of administered dose (lower in high oral dose group), C11H23O9Cl4P2 and C13H25O11Cl4P2
Any other information on results incl. tables
Table 7.1.1.1 Elemental composition of metabolites 1-4 determined by LC-MS
Elemental composition |
Difference from Parent |
|
Test substance – V6 |
C13H25O8Cl6P2 |
- |
Metabolite 1 |
C11H22O8Cl5P2 |
-C2H3Cl |
Metabolite 2 |
C13H24O10Cl5P2 |
-HCl + 2O |
Metabolite 3 |
C11H23O9Cl4P2 |
-C2H3Cl –Cl + OH |
Metabolite 4 |
C13H25O11Cl4P2 |
-HCl +2O –Cl +OH |
Metabolites 1-4 are either missing a chloroethyl moiety or the chlorine was replaced by an OH group, and further oxidised to a carboxyl group. The likely major metabolic pathways are the cleavage of one phosphate ester bond (metabolite 1) and the oxidation (substitution) of one chloroethyl sidechain to the corresponding hydroxyl and further oxidation to the carboxy group (metabolites 4 and 2, respectively). It is the opinion of the study director that metabolite 3 is likely to be a secondary metabolite of metabolite 1, undergoing a further hydroxylation on a second chloroethyl group.
- Administered dose was close to inteded dose for all animals
- No study or test substance related signs of toxicity or unusual behaviour were observed
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): no bioaccumulation potential based on study results
The test substance was rapidly and completely absorbed from the gastrointestinal tract. The test substance and its metabolites were distributed all over the body. No target organs except the organs of elimination were found. Low levels of the test substance were found in muscle and fat, indicating no bioaccumulation. Most of the radioactivity was excreted in faeces and to a minor extend in urine within 3 days after administration of the test substance. The test substance is metabolised almost completely to a relatively high number of different metabolites. The likely major metabolic pathways are the cleavage of one phosphate ester bond (metabolite 1) and the oxidation (substitution) of one chloroethyl sidechain to the corresponding hydroxyl and further oxidation to the carboxy group (metabolites 4 and 2, respectively). - Executive summary:
In a toxicokinetic study 2,2-bis(chloromethyl)trimethylene bis(bis(2-chloroethyl)phosphate) (chloroethyl-14C) was administered to 4 male and 4 female Wistar rats per group at dose levels of 15 and 600 mg/kg bw by oral administration and at a dose level of 15 mg/kg bw by intravenous dosing.
Elimination half life of the test substance was 102 -111h after oral dose and 99 -113 after intravenous dose. Bioavalability was around 142% after low oral dose and 47-55% after high oral dose. Absorption from the gastrointestinal tract is almost complete. Recovery of total radioactivity was low (around 80%, independently of dosing route and sex), possibly due to exhalation of small volatile compounds that could not be trapped in this study.
The test substance and its metabolites were distributed all over the body. No target organs except the organs of elimination were found. Low levels of the test substance were found in muscle and fat, indicating no bioaccumulation. The substance is completely metabolised to a number of different metabolites. The likely major metabolic pathways are the cleavage of one phosphate ester bond (metabolite 1) and the oxidation (substitution) of one chloroethyl sidechain to the corresponding hydroxyl and further oxidation to the carboxy group (metabolites 4 and 2, respectively). The majority of the radioactivity is excreted within 3 days in the faeces and to a minor extent in the urine in the form of metabolites. Volatile metabolites are likely exhaled, but could not be trapped in the study due to the high volatility.
This GLP metabolism study in the Wistar rat is classified valid without restrictions and satisfies the guideline requirement for a metabolism study according to OECD Guideline No.417.
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