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EC number: 203-585-2 | CAS number: 108-46-3
- 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 in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Findings are from a 90-day oral toxicity study conducted in accordance with OECD Guideline and under GLP conditions.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 004
- Report date:
- 2006
Materials and methods
- Objective of study:
- toxicokinetics
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: OECD TG 408
- Principles of method if other than guideline:
- Method: other: OECD TG 408
- GLP compliance:
- yes
Test material
- Reference substance name:
- Resorcinol
- EC Number:
- 203-585-2
- EC Name:
- Resorcinol
- Cas Number:
- 108-46-3
- Molecular formula:
- C6H6O2
- IUPAC Name:
- resorcinol
- Details on test material:
- Resorcinol (AO11), >95% purity
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
Administration / exposure
- Route of administration:
- oral: gavage
- Duration and frequency of treatment / exposure:
- 90 day(s)
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Males: 0, 40, 80 and 250 mg/kg/day Females: 0, 40, 80 and 250 mg/kg/day
- No. of animals per sex per dose / concentration:
- Males: 40 Females: 40
- Details on study design:
- The study was designed to comply with OECD Guideline No. 408, 21 September 1998.
See Section 5.4 for additional details. - Details on dosing and sampling:
- Three treated groups of 10 male and 10 female Sprague-Dawley rats received the test item, Resorcinol (A011), (batch No. 706030517), daily by gavage at 40, 80 or 250 mg/kg/day for 13 weeks. An additional group of 10 males and 10 females received only the vehicle (purified water) and acted as a control group. At 0 and 250 mg/kg/day (groups 1 and 4), six animals of each sex were treated for 13 weeks and then kept for a 4-week treatment-free period. Six animals of each sex in groups 2, 3 and 4 were used for toxicokinetic investigations; blood samples were taken from the animals on day 1 and in week 13 at the following time-points: 0.5, 1, 2, 4, 8 and 24 hours post-dosing, and each animal was sampled on three occasions.
Blood samples were taken from the animals on day 1 and in week 13 at the following time-points: . 0.5, 1, 2, 4, 8 and 24 hours post-dosing. For each time-point, three animals/sex/group were sampled (groups 2, 3 and 4), and each animal was sampled on three occasions. Venous blood (approximately 0.5 mL) was taken from the orbital sinus of the animals under light isoflurane anesthesia into a tube containing lithium heparin. The blood was centrifuged, and the plasma was kept frozen in individual tubes at -20°C until analysis after the development and validation of the analytical method. - Statistics:
- The toxicokinetic parameters were calculated, according to standard non-compartmental methods, using Excel 2000 software installed on a personal computer. The following parameters were determined: Cmax, maximal plasma concentration measured, tmax, time of occurrence of this maximal plasma concentration, AUCx-t, Area under the concentration-time curve (calculated according to the linear trapezoidal rule) from time 0 to the last quantifiable data-point.
Statistical analysis were peformed using the followng tests when appropriate: Kolmogorov-Lilliefors test, Dunn test, Mann-Whitney/Wilcoxon test, Student test, Bartlet test and Fischer test
Results and discussion
Toxicokinetic / pharmacokinetic studies
Toxicokinetic parametersopen allclose all
- Test no.:
- #1
- Toxicokinetic parameters:
- AUC: Day 1: at 40 mg/kg/day the AUC for males is 24 and females 25.7 (ug*h/mL).
- Test no.:
- #1
- Toxicokinetic parameters:
- Cmax: Day 1: at 40 mg/kg/day the Cmax in males is 1.45 ug/mL and 1.31 ug/mL in females.
- Test no.:
- #1
- Toxicokinetic parameters:
- Tmax: Day 1: The tmax for males is 1 and females 24 hours. The trend towards a plateau level, as several peaks may be noted at different time points from 0.5 to 24 hours.
- Test no.:
- #2
- Toxicokinetic parameters:
- AUC: Day 1: at 80 mg/kg/day the AUC in males is 6.25 ug*h/mL and 18 ug*h/mL in females.
- Test no.:
- #2
- Toxicokinetic parameters:
- Cmax: Day 1: at 80 mg/kg/day the Cmax in males is 1.13 ug/mL and 1.07 ug/mL in females.
- Test no.:
- #2
- Toxicokinetic parameters:
- Tmax: Day 1: The tmax for males is 2 and females 24 hours. The trend towards a plateau level, as several peaks may be noted at different time points from 0.5 to 24 hours.
- Test no.:
- #3
- Toxicokinetic parameters:
- AUC: Day 1: at 250 mg/kg/day the AUC in males is 6.12 ug*h/mL and 31.8 ug*h/mL in females.
- Test no.:
- #3
- Toxicokinetic parameters:
- Cmax: Day 1: at 250 mg/kg/day the Cmax in males is 2.37 ug/mL and 9.29 ug/mL in females.
- Test no.:
- #3
- Toxicokinetic parameters:
- Tmax: Day 1: The tmax for males is 0.5 and females 0.5 hours.
- Test no.:
- #4
- Toxicokinetic parameters:
- AUC: Week 13: at 40 mg/kg/day the AUC in males is NC and 0.15 ug*h/mL in females.
- Test no.:
- #4
- Toxicokinetic parameters:
- Cmax: Week 13: at 40 mg/kg/day the Cmax in males is NC and 0.59 ug/mL in females.
- Test no.:
- #4
- Toxicokinetic parameters:
- Tmax: Week 13: at 40 mg/kg/day, the tmax for males is NC and females 0.5 hours.
- Test no.:
- #5
- Toxicokinetic parameters:
- AUC: Week 13: at 80 mg/kg/day the AUC in males is 1.31 ug*h/mL and 3.61 ug*h/mL in females.
- Test no.:
- #5
- Toxicokinetic parameters:
- Cmax: Week 13: at 80 mg/kg/day the Cmax in males is 2.28 ug/mL and 4.48 ug/mL in females.
- Test no.:
- #5
- Toxicokinetic parameters:
- Tmax: Week 13: at 80 mg/kg/day, the tmax for males is 0.5 hours and females 0.5 hours.
- Test no.:
- #6
- Toxicokinetic parameters:
- AUC: Week 13: at 250 mg/kg/day the AUC in males is 10.9 ug*h/mL and 27.5 ug*h/mL in females.
- Test no.:
- #6
- Toxicokinetic parameters:
- Cmax: Week 13: at 250 mg/kg/day the Cmax in males is 17.9 ug/mL and 13.8 ug/mL in females.
- Test no.:
- #6
- Toxicokinetic parameters:
- Tmax: Week 13: at 250 mg/kg/day, the tmax for males is 0.5 hours and females 0.5 hours.
Metabolite characterisation studies
- Metabolites identified:
- not measured
Any other information on results incl. tables
When measured on day 1, for groups 2, 3 and 4, which
received the test item at 40, 80 and 250 mg/kg/day, plasma
levels of Resorcinol (A011) were quantifiable at least for
two animals at all time-points (except for group 2 males at
8 hours, for group 3 males at 24 hours and females at 4
hours, and for group 4 males at 24 hours). In contrast, in
week 13, plasma levels of the test item were generally below
the limit of quantification (0.5µg/mL) at all time-points
for group 2, and only quantifiable at 0.5 to 2 hours for groups 3 and 4.
For all treated groups, plasma levels of the test item
generally increased quickly from the first quantifiable
time-point at 0.5 hours on day 1 to reach a (first) maximum
Cmax at 0.5-2 hours. In some cases, a second Cmax was seen
at 8/24 hours. For groups 2 and 3 females, the second Cmax
noted at 24 hours actually was the highest observed plasma
level. The exposure on day 1, as measured by the Cmax and by
AUC0-t, showed no clear increase with test item dose-level.
The mean concentration of Resorcinol (A011) remained stable
over the 24 hour-period at 40 and 80 mg/kg/day, which may
suggest enterohepatic recycling of the test item. At 250
mg/kg/day, the Cmax was reached from 0.5 hour and plasma
levels gradually decreased thereafter.
In week 13, the first quantifiable time-point at 0.5 hours
was the maximal concentration. The exposure in week 13 (as
measured by the Cmax and by AUC0-t) increased with
dose-level in a supra linear manner.
Resorcinol (A011) plasma levels were characterized by a low
to moderate interanimal variability.
SAMPLING PERIOD: Day 1
40 mg/kg/day
Male Female
Kinetic parameter:
C(max) (µg/mL): 1.45 1.31
t(max) (h): 1(p) 24(p)
AUC(0-t) (µg*h/mL): 24.0 25.7
Ratio, C(max)/dose: 0.036 0.0327
Ratio, AUC/dose 0.600 0.643
80 mg/kg/day
Male Female
Kinetic parameter:
C(max) (µg/mL): 1.13 1.07
t(max) (h): 2(p) 24(p)
AUC(0-t) (µg*h/mL): 6.25 18.0
Ratio, C(max)/dose: 0.014 0.013
Ratio, AUC/dose 0.078 0.225
250 mg/kg/day
Male Female
Kinetic parameter:
C(max) (µg/mL): 2.37 9.29
t(max) (h): 0.5 0.5
AUC(0-t) (µg*h/mL): 6.12 31.8
Ratio, C(max)/dose: 0.009 0.037
Ratio, AUC/dose 0.024 0.127
where: p = trend towards a plateau level, as several peaks may be noted at different time-points from 05. to 24 hours.
SAMPLING PERIOD: Week 13
40 mg/kg/day
Male Female
Kinetic parameter:
C(max) (µg/mL): nc 0.59
t(max) (h): nc 0.5
AUC(0-t) (µg*h/mL): nc 0.15
Ratio, C(max)/dose: nc 0.015
Ratio, AUC/dose nc 0.004
80 mg/kg/day
Male Female
Kinetic parameter:
C(max) (µg/mL): 2.28 4.48
t(max) (h): 0.5 0.5
AUC(0-t) (µg*h/mL): 1.31 3.61
Ratio, C(max)/dose: 0.029 0.056
Ratio, AUC/dose 0.016 0.0451
250 mg/kg/day
Male Female
Kinetic parameter:
C(max) (µg/mL): 17.9 13.8
t(max) (h): 0.5 0.5
AUC(0-t) (µg*h/mL): 10.9 27.5
Ratio, C(max)/dose: 0.072 0.055
Ratio, AUC/dose 0.044 0.110
See Section 5.4 for additional details.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): other:
No clear conclusions were drawn by the authors regarding the dose, sex and time related observations, however, the rapid peaking of blood levels demonstrated rapid absorption after an oral dose, and the differences in blood levels at day 1 and week 13 suggest that the rats had adapted the way in which they handled resorcinol.
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