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EC number: 940-783-4 | 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Study period:
- no data
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The study was performed according to a method equivalent to OECD 417. No data on GLP. The publication describes the findings in detail.
Data source
Reference
- Reference Type:
- publication
- Title:
- [14C]bis(2-chloroethoxy)methane: Comparative absorption, distribution, metabolism and excretion in rats and mice.
- Author:
- Black, S.R., Decosta, K.S., Patel, P.R., Mathews, J.M.
- Year:
- 2 007
- Bibliographic source:
- Xenobiotica, April 2007; 37(4): 427-440
Materials and methods
- Objective of study:
- toxicokinetics
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 417 (Toxicokinetics)
- GLP compliance:
- yes
Test material
- Reference substance name:
- Bis(2-chloroethoxy)methane
- EC Number:
- 203-920-2
- EC Name:
- Bis(2-chloroethoxy)methane
- Cas Number:
- 111-91-1
- Molecular formula:
- C5H10Cl2O2
- IUPAC Name:
- 1-chloro-2-((2chloroethoxy)methoxy)ethane
- Details on test material:
- Nonradiolabeled BCM
Supplier: Pfaltz and Bauer (Waterbury, CT, USA)
Identity was confirmed by 'H-NMR and GC/MS analysis.
[14]BCM
Supplier: Wizard Laboratories (West Sacramento, CA, USA).
Uniformly radiolabeled in the ethyl groups, with a specific activity of 60.49 mCi/mmol (345.7 µCi/mg).
Radiochemical purity was confirmed by high performance liquid chromatography (HPLC) to be 294% using an isocratic system consisting of a Du Pont Zorbax Rx-C18 column (4.6 x 250mm, 5 pm, Mac-Mod 2 Analytical, Chadds Ford, PA, USA) and a mobile phase of acetonitrile:water (40:60, v:v)with a flow rate of 1 ml/min.
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- [14C]bis(2-chloroethoxy)methane
Test animals
- Species:
- other: rats and mice
- Strain:
- other: F344 and B6C3F1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: from Charles River Laboratories, Inc. (Raleigh, NC, USA)
- Age at study initiation: adult
- Weight at study initiation: rats 239-250g, mice 18-25 g
- Fasting period before study: no data
- Housing: individual glass metabolism cages post dosing
- Individual metabolism cages: yes
- Diet (e.g. ad libitum): Certified Purina Rodent Chow #5002, ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
- Acclimation period: no data
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20.5-23.9
- Humidity (%): 35-65
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): 12/12
IN-LIFE DATES: no data
Administration / exposure
- Route of administration:
- other: IV, oral or dermal
- Vehicle:
- other: saline, water or ethanol
- Details on exposure:
- IV
Male rats and male and female mice (n = 3-4) were dosed intravenously via the tail vein with [14C] BCM formulated in saline (1 mg/kg, 5-7 µCi, 1-2 ml/kg).
DERMAL
TEST SITE
- Area of exposure: intrascapular region
- % coverage: 4cm2 rats, 1cm2 mice.
- Type of wrap if used: Non-occlusive foam appliances fixed in place with Hollister's Medical Adhesive were used to prevent access to the dose site by rats; a metal tissue capsule fixed in place with cyanoacrylate adhesive, was used to prevent access by mice.
- Time intervals for shavings or clipplings: the exposure area was clipped the day prior to exposure.
REMOVAL OF TEST SUBSTANCE
- Washing (if done): The dose sites and appliances were washed with a series of soapy water-wetted (ca. 30ml of Liquid Ivory per liter) gauzes followed by water-wetted gauzes.
- Time after start of exposure: 6 hours
TEST MATERIAL
- Amount(s) applied (volume or weight with unit): 15-20µL for mice and 50µL for rats
- concentration (if solution): [14]BCM 0.1 and 10mg/kg, 0.3-12.6 µCi
VEHICLE
- Justification for use and choice of vehicle (if other than water): no data
- Amount(s) applied (volume or weight with unit): 15-20µL for mice and 50µL for rats
- Concentration (if solution): no data
- Lot/batch no. (if required): no data
- Purity:
USE OF RESTRAINERS FOR PREVENTING INGESTION: yes
ORAL
PREPARATION OF DOSING SOLUTIONS: formulated in water
VEHICLE
- Justification for use and choice of vehicle (if other than water): water
- Concentration in vehicle: 0.1 and 10 mg/kg, 0.7-9 µCi
- Amount of vehicle (if gavage): 5 ml/kg
- Lot/batch no. (if required): -
- Purity: -
HOMOGENEITY AND STABILITY OF TEST MATERIAL: no data - Duration and frequency of treatment / exposure:
- Single doses
Doses / concentrations
- Remarks:
- Doses / Concentrations:
see details on exposure
- No. of animals per sex per dose / concentration:
- IV n =3-4
oral n=4
dermal n=4 - Control animals:
- no
- Positive control reference chemical:
- Not applicable
- Details on study design:
- - Dose selection rationale: no data
- Rationale for animal assignment (if not random): no data - Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled : urine, faeces, blood, plasma, serum or other tissues, cage washes
- Time and frequency of sampling:
Urine and feces were collected separately up to 72 h post dosing into round-bottom flasks cooled with dry ice and were stored in the dark at -20°C until analyzed. Radiolabeled components in breath and/or volatized from skin were collected continuously for 72 h post dosing. Air from the metabolism cage (flow = 200-500 mllmin) passed first through two cryogenic traps containing 60 ml ethanol each and held at 4-C and -60°C, respectively, and then passed through two CO2 traps containing 500 ml 1 N NaOH each. At the end of each experiment, blood was withdrawn from anesthetized (as described above) animals into a heparinized syringe by cardiac puncture. Rats were euthanized by bilateral thoracotomy and mice by cervical dislocation while under anesthesia. Tissues were collected and analyzed for radioactivity to determine tissue distribution following i.v. administration. Carcasses and dermal dose site skin sections were digested in 2 N ethanolic sodium hydroxide. Scintillation cocktail was added to vials containing sections of the protective foam appliances and gauzes used to wash the skin. Metal tissue capsules used on mouse dermal studies were rinsed with acetone and aliquots of the rinsates were added to vials containing scintillation cocktail.
METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: urine, faeces, blood, plasma, serum or other tissues, cage washes
- Time and frequency of sampling: see above
- From how many animals: all animals, not pooled
- Method type(s) for identification: Alls samples = liquid scintillation spectrometry (LSS), Urinary metabolite profling and isolation = HPLC.
- Limits of detection and quantification: no data - Statistics:
- Means and standard deviations were calculated for the disposition of BCM. Values for test groups were compared by ANOVA followed by Dunnett's test.
Results and discussion
- Preliminary studies:
- No data
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- Absorption of BCM by male rats
Comparison of data obtained following intravenous vs. oral administration to male rats over a range of doses provided an estimate of the degree to which BCM-derived radioactivity was absorbed from the gastrointestinal tract.
I.v. and oral administration of BCM at lower and higher, but presumably non-toxic, doses (Table I) indicated that doses in this range were nearly completely absorbed from the gastrointestinal tract and rapidly excreted.
Absorption of BCM by male and female mice
Studies similar to those described above for rats conducted with both sexes of mice provided
an examination of the effects of both sex and species on the fate of BCM (Table II). A comparison of data in Tables I and II, describing the fate of similar doses of BCM following i.v. or oral gavage to male rats or male and female mice, indicates only minimal sex- or species-related differences in the fate of BCM.
Absorption of BCM by rats and mice following dermal administration
Studies of absorption of BCM by male rats and mice following administration of doses of
0.1 or 10 mg/kg to a protected area of skin indicated that, whereas volatilization and absorption onto the protective devices accounted for most of the dose, dermal absorption was significant. Further, absorption was not significantly altered by dose level in rats (Table III). Rats absorbed approximately 15% of each dose and as observed with oral and i.v. administration. Mice absorbed approximately 18% of the 10mg/kg dose. - Details on distribution in tissues:
- Tissue distribution in rats following i. v. administration
Male rats were euthanized at 0.25, 0.5, 1, 2, 4, and 8 h following i.v. administration of 1 mg/kg BCM, and selected tissues were collected for analysis of total radioactivity (Table IV).
*It is noted that scission of the ether linkage changes the specific activity of the resulting fragments. Therefore, the ng-equivalents/g tissue values were calculated assuming 4 labeled carbons. Equivalents representing fragments containing 1 or 2 carbon-14 per mole are underestimated by these ratios.
As anticipated from the rapid removal of radioactivity from blood CM-derived radioactivity was rapidly distributed to the tissues. Of the approximately 80% of the total dose recovered in the tissues assayed at 0.25 h post dosing, only about 2% was in blood. The highest concentrations of BCM-derived radioactivity were observed in the kidneys and are assumed to be related to the excretory function of these organs. The second highest concentrations were observed in the liver. Concentrations of BCM-derived radioactivity peaked in most tissues at, or prior to, the first time point, 0.25 h. In the liver, peak concentrations were observed approximately 0.5 h post dosing. The rapid decline of BCM-derived radioactivity from most tissues was consistent with the rapid excretion of BCM-derived radioactivity observed in earlier studies (Tables I and II). BCM-derived radioactivity accumulated in only one non-excretory tissue, thymus, where concentrations increased by almost three fold between 0.25 and 4 h post dosing and remained nearly constant for the next 4 h.
Most of the BCM-derived radioactivity in blood was unextractable within the first few minutes following dosing, and parent BCM was virtually undetectable in blood within approximately 5 h. In the present study only about 27% of the radioactivity was extracted from the liver at the 0.25 h time point, and extractable radioactivity in liver decreased to 4% within 4h. At 0.25 h approximately 60% of the radioactivity extracted from liver was parent BCM. This percentage decreased with time until only a trace of parent BCM was detected in the extracts of liver samples taken at 4 and 8 h post dosing. Approximately 85% of the radioactivity was extracted from thymus at the 0.25 h time point and approximately 44% of that radioactivity was parent BCM. However, even though the concentration of BCM-derived radioactivity in the thymus increased with time, extractable radioactivity decreased with time such that by 8 h only 9% of the radioactivity in the thymus was extractable. Further, the relative amounts of parent BCM in the radioactivity extracted from the thymus decreased with time such that only a trace was detected at 4 and 8 h post dosing.
- Details on excretion:
- Clearance of BCM by male rats
Comparison of data obtained following intravenous vs. oral administration to male rats over a range of doses provided an estimate of the rate and routes by which BCM-derived radioactivity was cleared from the body and the effects of dose on these parameters.
Intravenous administration of [14C]BCM at a presumably non-toxic and non-saturating dose, 1 mg/kg, in order to represent 100% absorption, indicated that BCM-derived radioactivity was rapidly excreted (Table I), primarily in urine, >95%, with a few per cent of the dose being completely metabolized and exhaled as CO2. Approximately 60% of the dose was excreted in 8 h, and excretion was nearly complete within 48 h. Less than 1% of the i.v. dose was recovered in the exhaled volatiles and feces combined.
Oral administration of BCM at lower and higher, but still presumably non-toxic, doses (Table I) indicated that doses in this range were nearly completely absorbed from the gastrointestinal tract and rapidly excreted. Total excretion in either case approached or exceeded 60% within 8 h. The rates and routes of excretion were very similar to those seen following i.v. administration and no evidence of saturation of gastrointestinal absorption or metabolism was observed over the dose range studied. The only statistically significant dose related differences observed were a slightly greater metabolism to 14CO2 and slightly less excretion in urine following administration of the higher dose.
Digestion and analysis of the carcasses 72 h following oral administration of 10mg/kg indicated minimal retention (-1.5% of the dose) of BCM-derived radioactivity. Because about 10% of the dose remains in the body at 24h post dosing, there is the potential for accumulation in a chronic study employing the standard
24-h dose intervals.
Clearance of BCM by male and female mice
Total excretion by both sexes of mice appears to have been slightly slower following an i.v. dose than observed with rats, 79 or 72% vs. 95% in 24 h. Mice may have also excreted a greater portion of the dose in feces than did rats; however, it is likely that this observation reflects, at least in part, the difficulty of obtaining effective separation of urine and feces in studies with mice. Mice also appear to have metabolized a somewhat greater portion of the dose to CO2 than did rats. Both species metabolized a greater portion of the higher dose to CO2. Similar to the data from rats, the total tissues of mice retained less than 1% of the dose 72h following dosing.
Clearance of BCM by rats and mice following dermal administration
Studies of absorption of BCM by male rats and mice following administration of doses of
0.1 or 10 mg/kg to a protected area of skin indicated that, in rats most (13.6-14.3% of the total dose) of the absorbed dermal dose was excreted in urine. In mice of the 10mg/kg dose 12.6% of that dose was recovered in urine. About 9% of the dose was recovered in urine of mice following dermal administration at 0.1 mg/kg.
Clearance of BCM-derived radioactivity following i. v. administration to rats
Following intravenous administration of 1 mg/kg to male rats, decline of BCM from blood was determined by analysis of blood collected from cannulated animals at time points up to 24 h.
Total BCM-derived radioactivity was rapidly removed from blood so that only about 2% of the dose remained in blood at the first time point (data not shown). These data further indicate that by 0.25 h post dosing most of the BCM-derived radioactivity in blood was in the form of metabolites or unextractable, possibly bound, radioactivity. The blood concentrations of both total radioactivity and parent BCM declined rapidly with time; however, the concentration of unextractable radioactivity initially increased to reach a maximum at approximately 2 h post dosing and then slowly declined over the course of the 24-h study.
The unextractable radioactivity accounted for most of the BCM-derived radioactivity at 4 h and at later time points. Similar experiments with female rats and male mice (data not shown) provided very similar results except that the blood of mice contained somewhat less parent BCM.
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- BCM metabolite isolation and identification
HPLC analysis of urine collected over 24h post dosing from rats administered p.o. or i.v. doses of BCM using the phosphate-buffered Hydrobond AQ system as described in Materials and methods, indicated the presence of five significant metabolites, R1-R5. Neither the pattern nor the relative amounts of the metabolites were greatly affected by the dose or route of BCM administration. Urine from mice dosed with BCM contained three major metabolites, M1-M3. In coelution experiments, M2 appeared to coelute with R4 and 11/13 coeluted with R5.
Incubation of urine from rats receiving an intravenous dose of BCM, 1 mg/kg, with acylase, sulfatase, or B-glucuronidase, failed to alter the chromatographic pattern of metabolites. It was thus assumed that the metabolites were not excreted as conjugates other than from reaction with GSH. HPLC analysis indicated that the major BCM metabolite, metabolite R3, coeluted with thiodiglycolic acid (TDGA), which is a known metabolite of 2-chloroacetaldehyde and 2-chloroethanol. The structure of this metabolite was further confirmed by electrospray MS in negative ion mode and co-chromatography with a known standard of TDGA on the Hydrobond AQ-C8 analytical system described in Materials and methods.
Any other information on results incl. tables
Table I. Cumulative excretion of radioactivity after[14C]BCM administration to male F-344 rats
Cumulative % dose recovered in
|
|||||
End of collection period Urine Breath volatiles CO2 Feces Total
|
|||||
Intravenous 1 mg kg-1) |
|
|
|
|
|
8h |
59.8 ± 8.3 |
0.18 ± 0.01 |
2.63 ± 0.95 |
|
62.6 ± 7.92 |
24h |
90.6 ± 3.4 |
0.20 ± 0.01 |
3.27 ± 1.09 |
0.50 ± 0.12 |
94.6 ± 2.80 |
48h |
95.7 ± 2.5 |
0.20 ± 0.02 |
3.51 ± 1.15 |
0.73 ± 0.21 |
100 ± 1.46 |
72h |
96.6 ± 2.3 |
0.21 ± 0.02 |
3.66 ± 1.18 |
0.76 ± 0.21 |
101 ± 1.29 |
Oral (0.1 mg kg-1) |
|
|
|
|
|
8h |
63.2 ± 1.7 |
0.05 ± 0.01 |
2.42 ± 0.45 |
|
65.7 ± 1.7 |
24h |
90.8 ± 0.7 |
0.06 ± 0.01 |
3.05 ± 0.58 |
0.87 ± 0.81 |
94.7 ± 0.7 |
48h |
93.7 ± 0.6 |
0.06 ± 0.01 |
3.27 ± 0.60 |
1.03 ± 0.80 |
98.0 ± 0.7 |
72h |
94.6 ± 0.6* |
0.07 ± 0.01 |
3.42 ± 0.60* |
1.08 ± 0.82 |
99.1 ± 0.6 |
Oral (10 mg kg-1) |
|
|
|
|
|
8h |
51.8 ± 9.1 |
0.09 ± 0.02 |
5.24 ± 1.48 |
|
57.2 ± 8.3 |
24h |
85.0 ± 1.7 |
0.11 ± 0.02 |
6.52 ± 1.86 |
0.37 ± 0.11 |
92.0 ± 1.3 |
48h |
89.0 ± 1.7 |
0.12 ± 0.02 |
6.94 ± 1.93 |
0.37 ± 0.10 |
96.5 ± 1.2 |
72h |
90.0 ± 1.9* |
0.12 ± 0.02 |
7.14 ± 1.97* |
0.41 ± 0.16 |
97.7 ± 1.5 |
n = 4
* Statistically significant difference between the two oral dose levels (p = 0.05)
Table II. Cumulative excretion of radioactivity 72h after[14C]BCM administration to B6C3F1mice.
% dose recovered in
|
|||||
End of collection period Urine Breath volatiles CO2 Feces Total
|
|||||
Intravenous 1 mg kg-1) male mice |
|
|
|
|
|
8h |
36.8 ± 26.1 |
0.91 ± 0.60 |
6.77 ± 0.91 |
|
44.5 ± 25.8 |
24h |
53.8 ± 27.9 |
0.97 ± 0.63 |
7.51 ± 1.10 |
16.7 ± 25.7 |
79.0 ± 11.0 |
48h |
58.6 ± 26.8 |
1.00 ± 0.65 |
8.32 ± 1.54 |
19.5 ± 25.7 |
87.5 ± 9.9 |
72h |
65.8 ± 26.5 |
1.01 ± 0.65 |
8.61 ± 1.55 |
20.3 ± 25.8 |
95.7 ± 4.4 |
Intravenous 1 mg kg-1) female mice |
|
|
|
|
|
8h |
27.0 ± 17.2 |
0.27 ± 0.02 |
3.52 ± 1.54 |
|
30.7 ± 16.4 |
24h |
52.0 ± 26.6 |
0.30 ± 0.03 |
4.17 ± 1.81 |
15.2 ± 10.2 |
71.7 ± 15.8 |
48h |
63.5 ± 25.2 |
0.31 ± 0.03 |
4.52 ± 1.98 |
17.3 ± 11.9 |
85.6 ± 132.1 |
72h |
71.5 ± 20.5 |
0.32 ± 0.03 |
4.70 ± 2.05 |
17.9 ± 12.5 |
94.4 ± 8.00 |
Oral (10 mg kg-1) male mice |
|
|
|
|
|
8h |
21.4 ± 19.7 |
0.08 ± 0.03 |
10.6 ± 1.3 |
|
32.0 ± 20.8 |
24h |
41.0 ± 17.1 |
0.10 ± 0.02 |
11.6 ± 1.5 |
20.6 ± 12.7 |
73.4 ± 9.3 |
48h |
45.6 ± 17.5 |
0.11 ± 0.03 |
12.4 ± 1.6 |
23.7 ± 14.9 |
81.8 ± 5.5 |
72h |
52.7 ± 17.2 |
0.11 ± 0.03 |
12.7 ± 1.6 |
24.5 ± 15.6 |
90.0 ± 2.8 |
Oral (10 mg kg-1) female mice |
|
|
|
|
|
8h |
9.35 ± 14.5 |
NC |
7.81 ± 2.04 |
|
17.2 ± 12.5 |
24h |
34.9 ± 21.7 |
NC |
9.46 ± 2.14 |
16.5 ± 9.3 |
60.9 ± 15.9 |
48h |
43.9 ± 24.8 |
NC |
10.3 ± 2.1 |
20.5 ± 11.5 |
74.7 ± 16.5 |
72h |
56.8 ± 18.4 |
NC |
10.7 ± 2.2 |
24.7 ± 14.2 |
92.2 ± 4.7 |
n = 4.
NC, not collected
Table III. Absortion of dermal doses of [14C]BMC in male F-344 rats andB6C3F1mice.
10 mg kg-1 0.1 mg kg-1
|
||||
Mice Rats Mice Rats
|
||||
Absorbed |
|
|
|
|
Urine |
12.59 ± 5.43 |
13.60 ± 1.88 |
8.94 ± 1.48 |
14.33 ± 5.38 |
CO2 |
1.10 ± 0.33 |
0.45 ± 0.15 |
0.42 ± 0.10 |
0.36 ± 0.15 |
Feces |
1.75 ± 1.01 |
0.60 ± 0.57 |
a |
0.27 ± 0.08 |
Tissues |
1.63 ± 1.80 |
0.55 ± 0.13 |
b |
0.51 ± 0.13 |
Dose site |
1.25 ± 1.59 |
0.24 ± 0.09 |
b |
0.25 ± 0.18 |
Total Absorbed |
18.30 ± 3.78 |
15.44 ± 2.55 |
9.36 ± 1.40 |
15.73 ± 5.82 |
Unabsorbedc |
19.33 ± 9.00 |
52.72 ± 10.09 |
7.23 ± 1.98 |
53.65 ± 9.97 |
Volatilized |
35.22 ± 15.63 |
18.73 ± 1.18 |
24.23 ± 4.06 |
18.78 ± 4.80 |
Total recovery |
72.87 ± 9.45 |
86.88 ± 12.26 |
40.82 ± 5.87 |
88.15 ± 14.60 |
n = 4. Data are mean ± SD of percentage dose recovered. Excreta were collected for 24 h post dosing. Tissues were sampled at 24 h post dosing.
aNo feces samples were collected.
bNo tissue samples were collected.
cRadioactivity recovered in the protective appliances and skin washes.
Table IV. Distribution of BCM-derived radioactivity in tissues of male rats following i.v. administration of [14C]BCM
Tissue |
0.25 h |
0.5 h |
1.0 h |
2.0 h |
4.0 h |
8.0 h |
Adipose |
1760 ± 214 |
1520 ± 221. |
663 ± 84.7 |
316 ± 21.2 |
237 ± 187 |
41.4 ± 4.39 |
Blood |
610 ± 18.6 |
529 ± 76.6 |
383 ± 53.2 |
343 ± 129 |
274 ± 41.0 |
154 ± 38.6 |
Brain |
50 ± 11.4 |
197 ± 31.4 |
103 ± 10.7 |
69.0 ± 8.37 |
74.8 ± 5.41 |
41.1 ± 4.83 |
Heart |
481 ± 12.8 |
401 ± 72.5 |
253 ± 12.2 |
200 ± 46.9 |
128 ± 24.9 |
47.8 ± 6.42 |
Kidney |
19 900 ± 1080 |
20 700 ± 88.1 |
16 000 ± 1400 |
9930 ± 2320 |
3930 ± 1810 |
1000 ± 60.2 |
Liver |
2420 ± 77.9 |
2800 ± 237 |
1790 ± 130 |
1670 ± 135 |
1200 ± 218 |
532 ± 78.0 |
Lung |
979 ± 71.0 |
889 ± 81.7 |
559 ± 65.0 |
783 ± 614 |
287 ± 39.9 |
149 ± 13.6 |
Muscle |
379 ± 11.1 |
415 ± 282 |
134 ± 18.4 |
82.2 ± 23.2 |
76.8 ± 27.9 |
30.5 ± 15.7 |
Skin |
641 ± 5.18 |
413 ± 51.1 |
307 ± 12.3 |
371 ± 152 |
334 ± 118 |
214 ± 66.5 |
Spleen |
396 ± 9.13 |
374 ± 26.1 |
397 ± 24.8 |
571 ± 9.35 |
476 ± 26.2 |
207 ± 13.5 |
Testis |
374 ± 63.8 |
277 ± 40.5 |
276 ± 22.3 |
393 ± 23.9 |
336 ± 28.7 |
104 ± 4.43 |
Thymus |
402 ± 78.4 |
278 ± 72.7 |
410 ± 32.0 |
842 ± 57.5 |
1140 ± 123 |
1040 ± 157 |
% Dose in tissues |
80.40 ± 2.33 |
70.38 ± 2.55 |
80.40 ± 2.33 |
33.11 ± 3.87 |
23.70 ± 5.53 |
10.30 ± 1.77 |
Data are ng BCM equivalents per gram tissue and are calculated based on the specific activity of the parent compound; mean ± SD; n = 3. Dose level was 1 mg kg-1.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): no bioaccumulation potential based on study results
The test substance is rapidly absorbed and excreted after oral and dermal exposure. The major metabolite (about 40% of the dose) of BCM in rat was isolated and identified as thiodiglycolic acid (TDGA). - Executive summary:
bis(2-Chloroethoxy)methane (BCM) is used primarily as a precursor in the synthesis of polysulfide elastomers. After administration of [ 14C]BCM , radioactivity is readily absorbed from the gastrointestinal tract and moderately absorbed through skin. Following absorption, BCM-derived radioactivity is rapidly distributed to all tissues, rapidly metabolized and excreted primarily in urine. Minimal effects of sex, species or dose in the range studied (0.1-1 0 mg kg) were observed on the fate of BCM in rats and mice after all routes of administration. The major metabolite (about 40% of the dose) of BCM in rat was isolated and identified as thiodiglycolic acid (TDGA) indicating that the ether linkage of BCM is cleaved to form 2-chloroethyl fragments that may be further metabolized to 2-chloracetaldehyde, conjugated with glutathione and the latter subsequently metabolized to TDGA. 2-chloroacetaldehyde has also been shown to be cardiotoxic, possibly accounting for BCM cardiotoxicity observed in repeated dose studies.
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