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EC number: 205-055-6 | CAS number: 132-27-4
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- Endpoint summary
- Appearance / physical state / colour
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- Density
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- Stability in organic solvents and identity of relevant degradation products
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- Additional physico-chemical properties of nanomaterials
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- Endpoint summary
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- 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
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- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
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- Additional toxicological data

Endpoint summary
Administrative data
Link to relevant study record(s)
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1983
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Objective of study:
- excretion
- metabolism
- GLP compliance:
- no
- Radiolabelling:
- no
- Species:
- rat
- Strain:
- Fischer 344/DuCrj
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Inc., Kanagawa, Japan
- Age at study initiation: 4 weeks old
- Diet: ad libitum except for the time in metabolism cages
- Water: ad libitum
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 24 - 26
- Humidity (%): 50 ± 5
- Air changes (per hr): 4
- Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Duration and frequency of treatment / exposure:
- daily for 136 days
- Dose / conc.:
- 2 other: % diet
- Remarks:
- The daily intake from the diet was estimated to be 280 mg for males and 180 mg for females according to the author
- No. of animals per sex per dose / concentration:
- 5
- Control animals:
- yes, concurrent no treatment
- Details on dosing and sampling:
- METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: urine, liver and kidney
- Time and frequency of sampling: urine was collected every 2 h for 6 h every day; liver and kidney were immediately removed at necropsy
- Method type(s) for identification: GC, GC-MS and HPLC
TREATMENT FOR CLEAVAGE OF CONJUGATES:
For the extraction of metabolites from the liver and kidneys, the tissue homogenate was digested with pronase and thereafter with glucuronidase - Type:
- excretion
- Results:
- 54.97% (± 7.98) and 39.04% (± 4.74) of the daily intake in males and females were excreted during 24 h in urine.
- Metabolites identified:
- yes
- Details on metabolites:
- High concentrations of phenolic metabolites, o-phenylphenol and 2,5-dihydroxybiphenyl, were found in the urine of rats of both sexes. Glucuronic acid conjugation was identified as the major route of OPP metabolism in rats.
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Objective of study:
- distribution
- excretion
- metabolism
- GLP compliance:
- no
- Radiolabelling:
- yes
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Japan
- Weight at study initiation: Approximately 180 g
- Acclimation period: At least 7 days
- Water: Drinking water containing glucose and saline during the time in Bollman cages, ad libitum - Route of administration:
- oral: unspecified
- Vehicle:
- water
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
14C-OPP (1.57 mCi/mmol) was obtained from the Radiochemical Centre, England, and its sodium salt was prepared by neutralization of 14C-OPP with sodium hydroxide solution. - Duration and frequency of treatment / exposure:
- single oral administration
- Dose / conc.:
- 250 mg/kg bw/day (nominal)
- Details on dosing and sampling:
- TOXICOKINETIC / PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled: urine, faeces, bile , blood, adipose, kidney, liver, stomach, intestine, brain and bladder
- Time and frequency of sampling: urine and faeces were collected daily for 7 days. Organ and tissue distributions (blood, adipose, kidney, liver, stomach, intestine, brain and bladder) were examined on Days 1, 3 and 7 after dosing using the liquid scintillation counting. For whole body autoradiography, rats received radiolabeled test substance (32.1 µCi) and were sacrificed at 0.5, 2, 6, 12 and 24 h thereafter.
METABOLITE CHARACTERISATION STUDIES
- Tissues and body fluids sampled: urine
- From how many animals: samples pooled from 4 rats after receiving the test substance in the diet for 2 weeks
- Method type(s) for identification: GC-MS for analysis and HPLC for purification - Type:
- excretion
- Results:
- 24 h after a single oral administration of the radiolabeled test substance 85.1% (± 2.7) were excreted via urine.
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- refer to analogue justification provided in IUCLID section 13
- Reason / purpose for cross-reference:
- read-across source
- Conclusions:
- No bioaccumulation potential was seen for the analogue substance based on study results. Applying the RA-approach similar results were expected for the target substance.
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- refer to analogue justification provided in IUCLID section 13
- Reason / purpose for cross-reference:
- read-across source
- Objective of study:
- metabolism
- Metabolites identified:
- yes
- Conclusions:
- A low bioaccumulation potential was determined for the analogue substance based on study results. Applying the RA-approach similar results were expected for the target substance.
- Endpoint:
- dermal absorption in vivo
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Justification for type of information:
- refer to analogue justification provided in IUCLID section 13
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Time point:
- 8 h
- Dose:
- 0.006 mg OPP/kg bw
- Parameter:
- percentage
- Absorption:
- 43.15 %
- Remarks on result:
- other: human
- Conclusions:
- Following 8 h of exposure OPP is rapidly absorbed via human skin with an absorption rate of approximately 43%. Applying the RA-approach, similar results were expected for the target substance.
Referenceopen allclose all
Almost all the dose was excreted in 48 h (Table 1). Most of the radioactivity was recovered in the urine and fecal excretion was small. Urinary excretion was very rapid for OPP-Na. About 25% and 50% of the dose were excreted in the urine up to 3 and 6 h, respectively (Table 2). Regarding the biliary excretion about one quarter of the dose was found in the bile 72 h after 14C-OPP-Na administration (Table 3). No significant retention in any organ and tissue tested was apparent following ingestion (Table 4).
Table 1: Excretion (%) of radioactivity in the urine up to 7 days after a single oral administration of 14C-labeled test substance
Days | 1 | 2 | 3 | 4-7 | Total |
Urine | 83.3 ± 1.1 | 1.9 ± 0.5 | 0.6 ± 0.1 | 0.8 ± 0.3 | 93.1 ± 1.7 |
Faeces | 2.1 ± 0.8 | 0.7 ± 0.5 | 0.2 ± 0.2 | 0.5 ± 0.2 |
Table 2: Excretion (%) of radioactivity in the urine up to 24 h after a single oral administration of 14C-labeled test substance
Time (hr) | 0-3 | 3-6 | 6-9 | 9-13 | 13-24 | Total |
Rat #1 | 29.6 | 17.6 | 16.4 | 15.6 | 5.4 | 84.6 |
Rat #2 | 29.7 | 17.8 | 20.4 | 8.7 | 11.3 | 88.0 |
Rat #3 | 14.4 | 39.4 | 12.9 | 9.8 | 6.3 | 82.7 |
Mean±S.D. | 24.6 ± 8.8 | 24.9 ± 12.5 | 16.6 ± 3.8 | 11.4 ± 3.7 | 7.6 ± 3.2 | 85.1 ± 2.7 |
Table 3: Excretion (%) of radioactivity in the bile after a single oral administration of 14C-labeled test substance
Time (hr) | 0-1 | 1-2 | 2-3 | 3-4 | 4-5 | 5-6 | 6-8 | 8-24 | 24-72 | Total |
Rat #1 | 1.4 | 2.7 | 3.0 | 3.4 | 5.7 | 4.2 | 5.5 | 1.3 | 0.3 | 27.5 |
Rat #2 | 1.1 | 2.0 | 3.5 | 9.3 | 6.8 | 1.8 | 0.6 | 0.6 | 0.3 | 26.0 |
Table 4: Relative Concentration (% dose/g x 100) of Radioactivity in the Rats after Single Oral Doses of 14C-labeled test substance
Organs | Day 1 (n=3) | Day 3(n=3) | Day 7 (n=4) |
Blood | 0.43 ± 0.05 | 0.18 ± 0.05 | 0.06 ± 0.02 |
Adipose | 0.05 ± 0.09 | 0.13 ± 0.18 | 0.01 ± 0.01 |
Kidney | 0.67 ± 0.27 | 0.70 ± 0.22 | 0.25 ± 0.06 |
Liver | 1.17 ± 0.15 | 1.01 ± 0.67 | 0.21 ± 0.06 |
Stomach | 0.55 ± 0.24 | 0.39 ± 0.67 | 0.01 ± 0.01 |
Intestine | 4.56 ± 2.75 | 0.88 ± 1.31 | 0.13 ± 0.10 |
Brain | 0.09 ± 0.07 | 0.04 ± 0.08 | 0.08 ± 0.06 |
Bladder | 0.24 ± 0.15 | 0.37 ± 0.34 | 0.03 ± 0.03 |
The follwing results were determined for the analogue substance 2-phenylphenol (OPP, CAS 90-43-7) in human:
OPP is rapidly absorbed via skin and
excreted predominantly via urine. The vast majority of absorbed material
is excreted within the first 24 h after application. The entire absorbed
dose is recovered in excreta, thus leaving no potential for systemic or
dermal accumulation.
The major metabolite identified in all urine samples analysed was the
sulphate conjugate of OPP. This metabolite accounted for 68.33% of the
absorbed dose. Conjugation of OPP with glucuronic acid was less
significant, accounting for only 3.46% of the absorbed dose.
Hydroxylation of the phenol or phenyl ring,
followed by conjugation was shown to be significant, with the
glucuronide conjugate of phenylhydroquinone (PHQ-Gluc) and
2,4´-dihydroxy biphenyl-sulfate (2,4´-DHB-Sulf) representing 14.34% and
12.35% of the absorbed dose, respectively. No sulphate conjugates of PHQ
was observed in any of the human urine samples analysed, contrary to
metabolism of OPP in rat and mouse, in which comparable amounts of both
PHQ-conjugates are found, independent from the applied dose.
Low levels of free OPP (0.5% of absorbed dose) and the glucuronide
conjugate (OPP-Gluc) were found in the early time intervals. Free OPP
was not observed in any of the analysed samples.
The following results were obtained for the analogue substance 2-phenylphenol (OPP; CAS 90-43-7):
Oral application in mice:
- 97 and 105% of the administered dose were recovered.
- The major excretory route was via the urine with 74 to 98% recovery of
the applied radioactivity. The faeces represent a minor excretory route,
with only 6-13 % recovery of the applied dose within 24 hours
post-dosing.
- Less than 1% of the radioactivity was found in the tissues and
carcass, suggesting a low potential for bioaccumulation.
- From the total of detected metabolites PHQ-glucuronide, PHQ-sulfate,
OPP-sulfate and OPP-glucuronide were the main excretion products.
- Qualitative metabolite differences were not observed in mice, however,
a dose-dependent quantitative difference in the extent of OPP sulfation
and glucuronidation was observed.
- The percentage excretion was not dose- dependent.
Oral application in rats:
- The metabolic profile was similar to the one observed in mice.
- The percentage excretion was not dose- and sex-dependent.
- OPP-sulfate was the main urinary metabolite accounting for 91.4 % of
the applied dose (for both dose groups)
- Two additional metabolite were found in urine of rats.
OPP was completely metabolised and rapid eliminated via the urine
predominantly as a sulphate and glucuronide conjugate of OPP.
Qualitatively the extent of metabolism was comparable between mice and
rats, although quantitative differences in the extent of OPP sulfation
and glucuronidation were seen between these species.
Description of key information
The target substance Na OPP was rapidly absorbed and excreted in the urine and faeces following oral administration. The source substance OPP is rapidly absorbed via skin and the gastrointestinal tract and widely distributed within the body. Thus, the bioavailability after oral intake is very high for both substances. Na OPP and OPP are completely metabolised and predominantly excreted via the urine and, to a minor degree, via faeces. There is only a low bioaccumulation potential noted in rodents, whereas for human, data indicate that there is no bioaccumulation potential.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
Experimental data regarding toxicokinetic behaviour are available for the target substance sodium 2-biphenylate (Na OPP, CAS 132-27-4) and for the source substance o-Phenylphenol (OPP, CAS 90-43-7) (McNett et al., 1997, Bartels, M. J. et al., 1997; Selim, S., 1996 and Bomhard, E. M. et al., 2002).
Sodium 2-biphenylate (Na OPP, CAS 132-27-4)
The metabolic profile of Na OPP was investigated in rats after sub-chronic oral administration (Nakao T. et al., 1983).
The elimination of various metabolites was investigated in 24 h urine samples over 136 days of five male and five female F344 rats administered 2% Na OPP in the feed (corresponding to at least 1000 mg/kg bw) (Bomhard, E. M. et al., 2002 and Nakao T. et al., 1983). Approximately 55% was eliminated in metabolized form by the males; approximately 40% by the females. Conjugates of glucuronic acid with OPP and phenylhydroquinone (PHQ) were identified as accounting for the major portion of the metabolites. Only 1% of the total phenolic metabolites eliminated was not conjugated with glucuronic acid. The concentration and distribution of the glucuronated metabolites were markedly different between males and females. Other metabolites were found neither in the urine, nor in the homogenized samples of liver and kidneys. The glucuronic acid content was reduced in the liver but not in the kidneys. The authors concluded that the two conjugates with glucuronic acid are the end products of the metabolic breakdown of SOPP in rats and that these metabolites are rapidly eliminated via the urine, because they were unable to detect either of these metabolites in the liver and kidney homogenates.
Excretion, organ distribution, and metabolic fate of 250 mg/kg bw 14C-Na OPP and 160 mg/kg bw 14C-OPP (specific activity: 1.6 mCi/mmol) were studied in four male F344 rats after a single oral administration (Bomhard, E. M. et al., 2002 and Sato M. et al., 1987). Another two male rats were cannulated to collect bile for 3 days after a single dose of 250 mg/kg 14C-Na OPP. Na OPP and OPP were rapidly excreted in the urine and faeces. About 83% of Na OPP and 88% of OPP appeared in the 24 h urine. Within 48 h about 93 and 98% were eliminated in the urine and feces, respectively. Biliary excretion amounted to about 25% of the dose within 3 days after Na OPP. Because the biliary excretion was larger than that in faeces, the authors presume intestinal reabsorption (enterohepatic circulation). No specific-organ affinity was apparent from the data of the tissue autoradiography. Thin layer chromatography (TLC) of the urine indicated the presence of conjugated metabolites only. No unchanged OPP or non-conjugated metabolites were detected. On the other band, in the urine of six male F344 rats fed 2% Na OPP-free OPP and PHQ were detected in addition. Furthermore, 2-phenyl-1,4-benzoquinone (PBQ) in a free state was detected as a minor metabolite.
O-Phenylphenol (OPP, CAS 90-43-7)
Oral absorption
In tests with rats and mice after oral dosing (McNett et al., 1997 and Bomhard, E. M. et al., 2002), 97 and 105% of the administered OPP (radiolabeled) were recovered after 24 and 48 h, respectively, indicating a fast and complete absorption of OPP via the gastrointestinal tract. Thus, OPP is rapidly bioavailable after oral dosing. Following oral uptake, OPP was shown to be completely metabolised and rapidly eliminated via the renal pathway, predominantly as a sulphate and glucuronide conjugate of OPP. Qualitatively the extent of metabolism was comparable between mice and rats, although quantitative differences in the extent of OPP sulfation and glucuronidation were seen between these species. Only 1% of the administered radioactivity was found in the tissues and carcass of rats, suggesting a low potential for bioaccumulation.
Dermal absorption
Following 8 h of exposure OPP is rapidly absorbed via human skin with an absorption rate of approximately 43% (Selim, S., 1996 and Bomhard, E. M. et al., 2002). The vast majority of absorbed material is excreted within the first 24 h after application via the renal pathway. The entire absorbed dose is recovered in excreta, thus leaving no potential for systemic or dermal accumulation (Bartels, M. J. et al., 1997; Selim, S., 1996 and Bomhard, E. M. et al., 2002). The major metabolite identified in all urine samples analysed was the sulphate conjugate of OPP. This metabolite accounted for 68.33% of the absorbed dose. Conjugation of OPP with glucuronic acid was less significant, accounting for only 3.46% of the absorbed dose. Hydroxylation of the phenol or phenyl ring, followed by conjugation was shown to be significant, with the glucuronide conjugate of phenyl-hydroquinone (PHQ-Gluc) and 2, 4´ dihydroxy biphenyl-sulfate (2,4´-DHB-Sulf) representing 14.34% and 12.35% of the absorbed dose, respectively. No sulphate conjugates of PHQ was observed in any of the urine samples analysed, contrary to metabolism of OPP in rat and mouse, in which comparable amounts of both PHQ-conjugates are found, independent from the applied dose. Low levels of free OPP (0.5% of absorbed dose) and the glucuronide conjugate (OPP-Gluc) were observed in the early time intervals. Free OPP was not observed in any of the analysed samples.
Conclusion
In summary, the target substance Na OPP was rapidly absorbed and excreted in the urine and faeces following oral administration. The source substance OPP is rapidly absorbed via skin and the gastrointestinal tract and widely distributed within the body. Thus, the bioavailability after oral intake is very high for both substances. Na OPP and OPP are completely metabolised and predominantly excreted via the urine and, to a minor degree, via faeces. There was only a low bioaccumulation potential noted in rodents, human data indicate that there is no bioaccumulation potential.
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