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EC number: 700-291-0 | CAS number: 1000701-92-7
- 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:
- other information
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study is comparable to OECD Guideline 427 with acceptable restrictions (partly limited documentation, e.g. no identification of metabolites).
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Percutaneous toxicokinetic and repeated cutaneous contact studies with ethylene glycol monohexyl ether
- Author:
- Ballantyne B et al.
- Year:
- 2 003
- Bibliographic source:
- J Appl Toxicol 23; 301-314
- Reference Type:
- secondary source
- Title:
- Unnamed
- Year:
- 2 005
Materials and methods
- Objective of study:
- toxicokinetics
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 417 (Toxicokinetics)
- Deviations:
- no
- GLP compliance:
- no
Test material
- Reference substance name:
- Hexylglycol (EGHE)
- IUPAC Name:
- Hexylglycol (EGHE)
- Reference substance name:
- 2-hexyloxyethanol
- EC Number:
- 203-951-1
- EC Name:
- 2-hexyloxyethanol
- Cas Number:
- 112-25-4
- Molecular formula:
- C8H18O2
- IUPAC Name:
- 2-(hexyloxy)ethanol
- Details on test material:
- - Analytical purity: 97.31%
- Specific activity: 2.1 mCi/mmol
- Locations of label: 1-hexyl and 1,2-ethanol positions
Constituent 1
Constituent 2
- Radiolabelling:
- yes
- Remarks:
- 14C
Test animals
- Species:
- rabbit
- Strain:
- New Zealand White
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Hazelton-Dutchland (Denver, PA)
- Age at study initiation: 9-10 weeks
- Weight at study initiation: 2-3 kg
- Housing: open rack-type metabolism cages
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: 5 d
ENVIRONMENTAL CONDITIONS
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- intravenous
- Vehicle:
- other: 0.9% saline
- Details on exposure:
- Rabbits were dosed through the marginal ear vein
- Duration and frequency of treatment / exposure:
- One intravenous injection
Doses / concentrations
- Remarks:
- Doses / Concentrations:
- Nominal dose: 1 and 10 mg/kg bw
- Actual dose: 0.972 and 10.08 mg/kg bw
- Radioactive dose (mean +/- SD): 8.6680 +/- 0.003 and 9.2561 +/- 0.0068 µCi/kg bw
- No. of animals per sex per dose / concentration:
- 4 males per dose
- Control animals:
- no
- Details on study design:
- - Dose selection rationale: based on preliminary intravenous LD50 study
- Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Samples: urine, faeces, blood & plasma, cage wash, carcass
- Time and frequency of sampling:
Blood & plasma: 2.5, 15 and 30 min and 1, 2, 4, 6, 12, 18, 24, 36 and 48 h
Urine: over 0–6 h, 6–12 h and thereafter at 12-h intervals up to 36 h
Faeces: over 24-h intervals
Cage wash: no details
- Plasma 14C concentrations were analyzed using computer-fitted, model-dependent methods. A bi-exponential equation was fitted to calculate mean values for plasma concentration–time data from four animals per dose using a non-linear least-squares data fitting program (RSTRIP; Micro-Math, Inc., Salt Lake City, UT). Parameters estimated included the distribution rate constant (kd), absorption rate constant (ka), elimination rate constant (ke), half-life (t1/2) for distribution, absorption and elimination, maximum plasma concentration (Cmax), time to Cmax (tmax), area under the curve through 48 h (AUC48), AUC to infinite time (AUC∞), apparent volume of distribution (Vd) and systemic clearance (Cltot).
METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: plasma, urine, faeces
- Time and frequency of sampling:
Plasma: 2.5, 15 and 30 min and 1, 2, 4, 6, 12, 18, 24, 36 and 48 h
Urine: over 0–6 h, 6–12 h and thereafter at 12-h intervals up to 36 h
Faeces: over 24-h intervals
- From how many animals: 4 per dose (plasma samples pooled)
- Method types for identification: liquid scintillation spectrometry, capillary gas chromatography coupled to a mass-selective detector (sensitivity 10 pg), HPLC separation and 14C quantitation with an in-line flow monitor
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on distribution in tissues:
- The plasma pharmacokinetic profiles at both i.v. doses are roughly superimposable, with a constant tenfold difference in plasma concentrations at a given time point. At both i.v. dosages there was a prolonged distribution phase and a moderate rate of elimination. Toxicokinetic parameters derived from fitted curves are given in Table 1 below. The distribution rate constants were relatively large. Elimination rate constants were small, with t1/2 32–40 h. The Cmax, AUC48 and AUC∞ valeus were dosage proportionate, suggesting first-order elimination processes for the dosage range studied. The Vd values were large, suggesting a broad tissue distribution. The systemic clearances were similar and close to the rabbit glomerular filtration rate of 10 ml/kg bw, further indicating that renal excretion is the major elimination route. Measurements of plasma EGHE concentrations by gas chromatography showed no detectable EGHE at 1 h or with subsequent samples up to 48 h.
- Details on excretion:
- A very high proportion of 14C was recovered in urine (78–83% over 48 h). The high recovery (93–102%) indicates low expired 14CO2. Rates were similar for the two dosages, and the majority was eliminated in the first 24 h postdosing.
For details see table 2 below.
Metabolite characterisation studies
- Metabolites identified:
- not measured
- Details on metabolites:
- Using urine HPLC chromatograms and a C8 column, free EGHE could not be detected and most of the 14C eluted as a single peak at the column void volume (ca. 1–2 min). Using an Aminex column it was possible to separate 3–4 major peaks (8.75, 9.5, 11.25 and 15.75 min) and 1–4 scattered minor peaks.
Any other information on results incl. tables
Table 1: Toxicokinetic parameter estimates for a two-compartment open model of plasma total radioactivity following intravenous dosing of New Zealand White rabbits with EGHE:
Parameter |
Symbol |
Estimated value |
|
1 mg/kg bw |
10 mg/kg bw |
||
Distribution rate constant (min-1) |
kd |
0.04097 |
0.01723 |
Distribution half-life (min) |
t1/2 |
19.92 |
40.23 |
Elimination rate constant (min-1) |
ke |
0.000293 |
0.00360 |
Elimination half-life (min) |
t1/2 |
2368 |
1925 |
Maximal plasma concentration (µg g-1) |
Cmax |
5.10 |
42.49 |
Time to Cmax (min) |
tmax |
0.0 |
0.0 |
AUC to 48 h (µg g-1 min) |
AUC48 |
288.7 |
3958.5 |
AUC to infinite time (µg g-1 min) |
AUC∞ |
357.4 |
4241.3 |
Apparent distribution volume (ml) |
Vd |
43640 |
32610 |
Systemic clearance (ml min-1) |
Cltot |
12.78 |
11.78 |
Table 2: Disposition of radiolabel in male New Zealand White rabbits following intravenous dosing with [14C]EGHE:
Fraction |
Time (h) |
Percentage recovered dose (mean ± SD; n=4) |
|
1 mg/kg bw |
10 mg/kg bw |
||
Urine |
0-48 |
83.05 +/-6.96 |
78.38 +/-3.04 |
Feces |
0-24 |
1.18 +/-0.76 |
1.06 +/-0.56 |
24-48 |
0.43 +/-0.46 |
0.23 +/-0.12 |
|
0-48 |
1.61 +/-0.44 |
1.28 +/-0.60 |
|
Cage wash |
3.12 +/-1.54 |
6.07 +/-1.56 |
|
Carcass |
4.93 +/-3.52 |
16.22 +/-3.24 |
|
Total % radioactivity recovered |
93.10 +/-2.17 |
102.40 +/-2.59 |
Applicant's summary and conclusion
- Conclusions:
- The i.v. toxicokinetic studies in rabbits showed first-order toxicokinetics in the range 1 -10 mg/kg bw. EGHE is rapidly and extensively metabolized, with elimination occurring mainly by renal excretion.
- Executive summary:
The study is comparable to OECD Guideline 427 with acceptable restrictions (partly limited documentation, e.g. no identification of metabolites).
The toxicokinetics of EGHE was investigated in New Zealand White rabbits by intravenous (i.v.) dosing. Given i.v. to male rabbits (1.0 and 10 mg/kg bw) [14C]EGHE demonstrated first-order kinetics. Carbon-14 was eliminated mainly in urine (78–83%) as metabolites, with no free EGHE. The plasma free EGHE concentration declined very rapidly post-dosing and was not detectable by 1 h.
Conclusion: The i.v. toxicokinetic studies in rabbits showed first-order toxicokinetics in the range 1 -10 mg/kg bw. EGHE is rapidly and extensively metabolized, with elimination occurring mainly by renal excretion.
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