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Diss Factsheets

Administrative data

Key value for chemical safety assessment

Effects on fertility

Description of key information

NOAEL was estimated to be 390.5 mg/kg bw when Sprague-Dawley male and female rats were orally exposed with 4-(2-Aminoethyl)phenol. 

Thus, as per criteria of CLP regulation, 4-(2-Aminoethyl)phenol can be not classified for reproductive toxicity.    

Link to relevant study records
Reference
Endpoint:
toxicity to reproduction
Type of information:
(Q)SAR
Adequacy of study:
weight of evidence
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
results derived from a valid (Q)SAR model and falling into its applicability domain, with limited documentation / justification
Justification for type of information:
Data is predicted using OECD QSAR toolbox version 3.4 and the supporting QMRF report has been attached
Qualifier:
according to guideline
Guideline:
other: as below
Principles of method if other than guideline:
Prediction is done using QSAR Toolbox version 3.4
GLP compliance:
not specified
Limit test:
no
Species:
rat
Strain:
Sprague-Dawley
Sex:
male/female
Route of administration:
oral: gavage
Type of inhalation exposure (if applicable):
not specified
Vehicle:
ethanol
Details on exposure:
not specified
Details on mating procedure:
not specified
Analytical verification of doses or concentrations:
not specified
Duration of treatment / exposure:
56 days for F0 and 98 days for F1
Frequency of treatment:
Daily
Details on study schedule:
not specified
Dose / conc.:
390.5 mg/kg bw/day
No. of animals per sex per dose:
26 rats/sex/dose
Control animals:
yes, concurrent no treatment
Details on study design:
not specified
Positive control:
not specified
Parental animals: Observations and examinations:
not specified
Oestrous cyclicity (parental animals):
not specified
Sperm parameters (parental animals):
not specified
Litter observations:
not specified
Postmortem examinations (parental animals):
not specified
Postmortem examinations (offspring):
not specified
Statistics:
not specified
Reproductive indices:
not specified
Offspring viability indices:
not specified
Clinical signs:
not specified
Dermal irritation (if dermal study):
not specified
Mortality:
not specified
Body weight and weight changes:
not specified
Food consumption and compound intake (if feeding study):
not specified
Food efficiency:
not specified
Water consumption and compound intake (if drinking water study):
not specified
Ophthalmological findings:
not specified
Haematological findings:
not specified
Clinical biochemistry findings:
not specified
Urinalysis findings:
not specified
Behaviour (functional findings):
not specified
Immunological findings:
not specified
Organ weight findings including organ / body weight ratios:
not specified
Histopathological findings: non-neoplastic:
not specified
Histopathological findings: neoplastic:
not specified
Other effects:
not specified
Reproductive function: oestrous cycle:
not specified
Reproductive function: sperm measures:
not specified
Reproductive performance:
not specified
Dose descriptor:
NOAEL
Effect level:
390.5 mg/kg bw/day (actual dose received)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
reproductive performance
Remarks on result:
other: No effect on reproduction
Critical effects observed:
not specified
System:
other: not specified
Organ:
not specified
Treatment related:
not specified
Dose response relationship:
not specified
Relevant for humans:
not specified
Clinical signs:
not specified
Dermal irritation (if dermal study):
not specified
Mortality / viability:
not specified
Body weight and weight changes:
not specified
Food consumption and compound intake (if feeding study):
not specified
Food efficiency:
not specified
Water consumption and compound intake (if drinking water study):
not specified
Ophthalmological findings:
not specified
Haematological findings:
not specified
Clinical biochemistry findings:
not specified
Urinalysis findings:
not specified
Sexual maturation:
not specified
Organ weight findings including organ / body weight ratios:
not specified
Gross pathological findings:
not specified
Histopathological findings:
not specified
Other effects:
not specified
Behaviour (functional findings):
not specified
Developmental immunotoxicity:
not specified
Dose descriptor:
other: not specified
Generation:
other: not specified
Based on:
not specified
Sex:
not specified
Basis for effect level:
other: not specified
Remarks on result:
other: not specified
Critical effects observed:
not specified
System:
other: not specified
Organ:
not specified
Treatment related:
not specified
Dose response relationship:
not specified
Relevant for humans:
not specified
Reproductive effects observed:
not specified
Treatment related:
not specified
Relation to other toxic effects:
not specified
Dose response relationship:
not specified
Relevant for humans:
not specified

The prediction was based on dataset comprised from the following descriptors: NOAEL
Estimation method: Takes average value from the 5 nearest neighbours
Domain  logical expression:Result: In Domain

((((((((((("a" or "b" or "c" or "d" or "e" )  and ("f" and ( not "g") )  )  and ("h" and ( not "i") )  )  and ("j" and ( not "k") )  )  and ("l" and ( not "m") )  )  and ("n" and ( not "o") )  )  and "p" )  and "q" )  and "r" )  and "s" )  and ("t" and "u" )  )

Domain logical expression index: "a"

Referential boundary: The target chemical should be classified as Primary amines by OECD HPV Chemical Categories

Domain logical expression index: "b"

Referential boundary: The target chemical should be classified as Aliphatic Amines AND Phenols (Acute toxicity) by US-EPA New Chemical Categories

Domain logical expression index: "c"

Referential boundary: The target chemical should be classified as Michael addition AND Michael addition >> P450 Mediated Activation to Quinones and Quinone-type Chemicals AND Michael addition >> P450 Mediated Activation to Quinones and Quinone-type Chemicals >> Alkyl phenols by DNA binding by OECD

Domain logical expression index: "d"

Referential boundary: The target chemical should be classified as Weak binder, OH group by Estrogen Receptor Binding

Domain logical expression index: "e"

Referential boundary: The target chemical should be classified as AN2 AND AN2 >> Michael-type addition to quinoid structures  AND AN2 >> Michael-type addition to quinoid structures  >> Substituted Phenols by Protein binding by OASIS v1.4

Domain logical expression index: "f"

Referential boundary: The target chemical should be classified as Weak binder, OH group by Estrogen Receptor Binding

Domain logical expression index: "g"

Referential boundary: The target chemical should be classified as Non binder, non cyclic structure by Estrogen Receptor Binding

Domain logical expression index: "h"

Referential boundary: The target chemical should be classified as Weak binder, OH group by Estrogen Receptor Binding

Domain logical expression index: "i"

Referential boundary: The target chemical should be classified as Non binder, without OH or NH2 group by Estrogen Receptor Binding

Domain logical expression index: "j"

Referential boundary: The target chemical should be classified as Weak binder, OH group by Estrogen Receptor Binding

Domain logical expression index: "k"

Referential boundary: The target chemical should be classified as Very strong binder, OH group by Estrogen Receptor Binding

Domain logical expression index: "l"

Referential boundary: The target chemical should be classified as Arylethanamine-like derivatives (11a) AND Known precedent reproductive and developmental toxic potential by DART scheme v.1.0

Domain logical expression index: "m"

Referential boundary: The target chemical should be classified as Non-steroid nucleus derived estrogen receptor (ER) and androgen receptor (AR) by DART scheme v.1.0

Domain logical expression index: "n"

Referential boundary: The target chemical should be classified as Arylethanamine-like derivatives (11a) AND Known precedent reproductive and developmental toxic potential by DART scheme v.1.0

Domain logical expression index: "o"

Referential boundary: The target chemical should be classified as Toluene and small alkyl toluene derivatives (8a) by DART scheme v.1.0

Domain logical expression index: "p"

Referential boundary: The target chemical should be classified as No superfragment by Superfragments ONLY

Domain logical expression index: "q"

Similarity boundary:Target: NCCc1ccc(O)cc1
Threshold=30%,
Dice(Atom centered fragments)
Atom type; Count H attached; Hybridization

Domain logical expression index: "r"

Similarity boundary:Target: NCCc1ccc(O)cc1
Threshold=50%,
Dice(Atom centered fragments)
Atom type; Count H attached; Hybridization

Domain logical expression index: "s"

Similarity boundary:Target: NCCc1ccc(O)cc1
Threshold=60%,
Dice(Atom centered fragments)
Atom type; Count H attached; Hybridization

Domain logical expression index: "t"

Parametric boundary:The target chemical should have a value of log Kow which is >= 0.0859

Domain logical expression index: "u"

Parametric boundary:The target chemical should have a value of log Kow which is <= 4.18

Conclusions:
NOAEL was estimated to be 390.5 mg/kg bw when Sprague-Dawley male and female rats were orally exposed with 4-(2-Aminoethyl)phenol.
Executive summary:

In a prediction done by SSS (2018) using the OECD QSAR toolbox with log kow as the primary descriptor, the reproductive toxicity was estimated for 4-(2-Aminoethyl)phenol. The NOAEL was estimated to be 390.5 mg/kg bw when Sprague-Dawley male and female rats were orally exposed with 4-(2-Aminoethyl)phenol.

Effect on fertility: via oral route
Endpoint conclusion:
no adverse effect observed
Dose descriptor:
NOAEL
309.5 mg/kg bw/day
Study duration:
subchronic
Species:
rat
Quality of whole database:
Data is Klimisch 2 and from OECD QSAR toolbox (2018)
Effect on fertility: via inhalation route
Endpoint conclusion:
no study available
Effect on fertility: via dermal route
Endpoint conclusion:
no study available
Additional information

Reproductive toxicity:

In different studies, 4-(2-Aminoethyl)phenol has been investigated for reproductive toxicity to a greater or lesser extent. Often are the studies based on in vivo experiments and estimation in rodents, i.e. most commonly in rats for 4-(2-Aminoethyl)phenol along with the study available on structurally similar read across substance (4-methoxyphenyl)acetic acid (CAS no 104-01-8) and (4-methoxyphenyl)acetic acid (CAS no 104-01-8). The predicted data using the OECD QSAR toolbox has also been compared with the experimental studies. 

In a prediction done by SSS (2018) using the OECD QSAR toolbox with log kow as the primary descriptor, the reproductive toxicity was estimated for 4-(2-Aminoethyl)phenol. The NOAEL was estimated to be 390.5 mg/kg bw when Sprague-Dawley male and female rats were orally exposed with 4-(2-Aminoethyl)phenol. 

In another experimental study conducted by Hagan et al (Food Cosmetic Toxicology, Vol 5, pp. 141-157. 1967) on structurally similar read across phenethyl phenylacetate (CAS 102-20-5), 10 male and female Osborne-Mendel rats were treated with phenethyl phenylacetate in the concentration 0 and 500 mg/kg bw/day orally by gavage from 17 weeks. No treatment-related clinical signs and premature deaths were observed. No relevant necropsy findings were noted. No effects on reproductive organ i.e testes was noted in treated rats at 500 mg/kg bw. Hence Now Observed Adverse Effect Level (NOAEL) for reproductive toxicity was considered to 500 mg/kg/day, when male and female Osborne-Mendel rats were treated with phenethyl phenylacetate (102-20-5) orally for 17 weeks.

Further supported by experimental study conducted by Kotin wt al (National Cancer Institute Division of Cancer Cause &Prevention Carcinogenesis Program Bethesda,Maryland,1968) on structurally similar read across (4-methoxyphenyl)acetic acid (CAS no 104-01-8), B6C3F1 female mice were treated with (4-methoxyphenyl)acetic acid in the concentration of 0 and 215 mg/kg bw/day in 0.5% gelatin for 7 to 28 day and after dose is administer through diet at 560 ppm for 18 months. Body weight gain was observed with the increase in duration of treatment. No gross pathological changes were observed in treated female mice. In addition, no fibroadenoma and carcinoma mammary gland were observed in treated female mice as compared to control. Therefore, NOAEL was considered to be > 215 mg/kg bw when B6C3F1 female mice by using (4-methoxyphenyl) acetic acid for 18 months.

Thus, based on the above study and predictions on 4-(2-Aminoethyl)phenol and its read across substances, it can be concluded that NOAEL value is 309.5 mg/kg bw with no effect on reproduction. Thus, as per criteria of CLP regulation, 4-(2-Aminoethyl)phenol can be not classified for reproductive toxicity.

Effects on developmental toxicity

Effect on developmental toxicity: via oral route
Endpoint conclusion:
no study available
Effect on developmental toxicity: via inhalation route
Endpoint conclusion:
no study available
Effect on developmental toxicity: via dermal route
Endpoint conclusion:
no study available

Justification for classification or non-classification

Based on the above study and predictions on 4-(2-Aminoethyl)phenol and its read across substances, it can be concluded that NOAEL value is 309.5 mg/kg bw with no effect on reproduction. Thus, as per criteria of CLP regulation, 4-(2-Aminoethyl)phenol can be not classified for reproductive toxicity.    

Additional information