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EC number: 284-325-5 | CAS number: 84852-15-3
- 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
Toxicity to reproduction
Administrative data
- Endpoint:
- fertility, other
- Remarks:
- based on test type (migrated information)
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Meets generally accepted scientific standards, well documented and acceptable for assessment.
Data source
Reference
- Reference Type:
- publication
- Title:
- Reproductive Toxicity of Male Mice after Exposure to Nonylphenol
- Author:
- El-Dakdoky MH, Helal MAM
- Year:
- 2 007
- Bibliographic source:
- Bull Environ Contam Toxicol (2007) 79:188–191
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- NP is applied by intraperitoneal injection of 0, 21.25 and 42.50 mg/kg bw/day to male mice for 35 consecutive days. These males were subsequently mated with untreated females. Effects of NP on sperm characteristics, fertility index, histopathological and biochemical changes related to oxidative stress in testes were examined.
- GLP compliance:
- not specified
- Limit test:
- no
Test material
- Reference substance name:
- p-nonylphenol
- EC Number:
- 203-199-4
- EC Name:
- p-nonylphenol
- Cas Number:
- 104-40-5
- IUPAC Name:
- 4-nonylphenol
Constituent 1
Test animals
- Species:
- mouse
- Strain:
- Swiss
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Central Animal House of the National Research Center, Egypt
- Age at study initiation: (P) 5 w
- Weight at study initiation: (P) Males and Females: 25-27 g;
- Fasting period before study: no data
- Housing: no data
- Diet (e.g. ad libitum): standard chow
- Water (e.g. ad libitum): no further details reported
- Acclimation period: no data
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 23-25
- Humidity (%): 50-65
- Air changes (per hr): no data
- Photoperiod (hrs dark / hrs light): 12:12
IN-LIFE DATES: From: To: no data
Administration / exposure
- Route of administration:
- intraperitoneal
- Vehicle:
- corn oil
- Details on mating procedure:
- - M/F ratio per cage: 1/1 with untreated female
- Length of cohabitation: 7 days
- Proof of pregnancy: vaginal plug or sperm in vaginal smear referred to as day 1 of pregnancy - Duration of treatment / exposure:
- 35 days (males only)
- Frequency of treatment:
- daily (males only)
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 21.25, 42.5 mg/kg/d
Basis:
- No. of animals per sex per dose:
- 10 male mice per dose group
- Control animals:
- yes, concurrent no treatment
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale (-> pilot study):
In the present investigation, the acute intraperitoneal (i.p.) LD 50 of nonylphenol (NP) was calculated for adult male mice as 170 mg/kg b.wt according to the simplified method of evaluating dose effect experiments (Litchfield and Wilcoxon 1949).
In order to determine the minimal doses of NP capable of inducing any toxic effect on testis, daily doses of 5.31, 10.62, 21.25, and 42.50 mg/kg b.wt equivalent to 1/20, 1/10, 1/8 and 1/4 LD 50 of NP were administered intraperitonealy for 2 weeks.
The doses of 5.31 and 10.62 mg/kg were neglected as they did not exert any toxic effect on male reproductive organs weight and sperm characteristics. - Positive control:
- Not applicable
Examinations
- Sperm parameters (parental animals):
- - Parameters examined in P male parental generations:
testis weight, epididymis weight, weight of seminal vesicles
- Determination of sperm motility:
Concentration and sperm morphological abnormalities, the epididymal content of each mouse was obtained after cutting the tail of epididymis and squeezing it gently in sterile clean watch glass and examined - Postmortem examinations (parental animals):
- SACRIFICE
- Male animals: After mating trials, male mice of all groups were anesthetized and sacrificed; the reproductive organs (testes, epididymis and seminal vesicles) were removed and weighed.
Testes examination: One of the testes was homogenized, the homogenates were centrifuged and the supernatant was separated and used for oxidative stress analysis. Malondialdehyde (MDA) concentration, Glutathione reduced (GSH) level, and superoxide dismutase (SOD) activities were assayed.
Histological examination: the right testes were fixed in 10% neutral formalin, dehydrated in graded series of alcohol, embedded in a paraffin wax, sectioned at 5–7 µm and stained with hematoxyline and eosin. The diameter and germinative cell layer thickness of the seminiferous tubule (ST) from ten different areas of testes were measured by the aid of ‘‘Leica Q500 MC’’ image analyzer computer system.
- Maternal animals: Females were isolated and kept under observation till 18th day of gestation. Pregnant mice were sacrificed on the day 19 of gestation. The uteri were dissected and the implantation sites, number of viable, resorbed and dead fetuses were recorded. The fetuses were examined morphologically to determine any external abnormalities.
GROSS NECROPSY
- Gross necropsy consisted of external and internal examinations including the cervical, thoracic, and abdominal viscera.
HISTOPATHOLOGY / ORGAN WEIGHTS
The tissues indicated in Table 1 were prepared for microscopic examination and weighed, respectively. - Statistics:
- The data obtained were subjected to statistical analysis. All values were given as mean standard error of measurement (S.E.). To determine the differences among all groups in the whole parameters one-way analysis of variance (ANOVA) and post hoc LSD analysis were performed using the SPSS/PC computer program (version 10). Statistical significance was determined at the level of significance of p < 0.05.
Results and discussion
Results: P0 (first parental generation)
Effect levels (P0)
- Dose descriptor:
- LOAEL
- Effect level:
- 42 mg/kg bw/day (actual dose received)
- Sex:
- male
- Basis for effect level:
- other: Effects on reproductive organs weight and sperm characteristics (count and motility), testicular MDA, GSH, and SOD; no effect on mating behavior, male fertility and the developed fetuses
Overall reproductive toxicity
- Reproductive effects observed:
- not specified
Any other information on results incl. tables
The values of reproductive organs weight and sperm characteristics are shown in Tables 1 and 2, respectively.
Table 1: Testis, epididymis and seminal vesicle weights (mg)
Parameters |
Right testis |
Right epididymis |
Seminal vesicle |
Control |
97.3±4.6 |
48.4±1.8 |
166.0±6.9 |
Oil |
96.6±5.3 |
46.7±2.8 |
165.4±6.6 |
21.25 mg/kg NP |
92.1±3.6 |
43.0±3.8 |
164.1±6.1 |
42.50 mg/kg NP |
81.7±2.9* |
39.7±2.4* |
161.8±4.8 |
* Indicates significant compared to control group (p < 0.05)
Table 2: Epididymal sperm count, sperm motility and abnormal sperm rate
Parameters |
Sperm count (x 106) sperm/m3 |
Sperm motility (%) |
Sperm abnormal rate (%) |
Control |
27.6±0.54 |
85.9±1.6 |
4.23±0.30 |
Oil |
27.1±1.02 |
85.7±0.6 |
3.80±0.12 |
21.25 mg/kg NP |
26.3±0.73 |
78.3±2.8* |
4.60±0.37 |
42.50 mg/kg NP |
25.6±0.66* |
72.7±2.6** |
4.90±0.36 |
*, ** Indicates significant compared to control group at (p < 0.05), (p < 0.01), respectively.
The higher dose of NP significantly reduced testes and epididymis weight and sperm count (p < 0.05) and motility (p < 0.01), while the lower dose only decreased significantly sperm motility (p < 0.05) in comparing to controls.
No changes in the seminal vesicles weight and in the sperm abnormal rate were noticed in all experimental groups.
Male exposure to 1/8 and 1/4 LD 50 NP for 35 days had no effect on mating behavior or pregnancy rate. Neither causes any significant changes in number of implantation per litter (No. impl./litter), live fetuses, fetal body weight or external visible abnormalities when compared to the control groups (Table 3). These may be attributed to NP had limited toxic effect on spermatogenesis which was not extended to the fertility.
Table 3: Mating index, fertility index and paternal effect on fetuses
Parameters |
Mating (%) |
Fertility (%) |
No. impl./litter |
Live fetuses |
Fetal body weight (g) |
Control |
100 |
100 |
8.3±0.4 |
91.0±5.71 |
1.35±0.03 |
Oil |
85.7 |
100 |
7.2±0.9 |
89.2±6.64 |
1.33±0.07 |
21.25 mg/kg NP |
85.7 |
100 |
7.2±1.1 |
89.0±5.09 |
1.25±0.06 |
42.50 mg/kg NP |
85.7 |
100 |
7.6±0.8 |
86.1±5.20 |
1.23±0.07 |
The diameter and thickness of the germinative cell layer of ST were significantly smaller in the NP exposed groups even at the low dose level (Table 4). These histological measurements further supported the finding of a low testicular mass.
Table 4: Mean values of diameter size and germinative cell layer thickness of seminiferous tubules in testes tissue (µm)
Parameters |
Diameter size |
Germinative cell layer thickness |
Control |
237.7±2.81 |
58.2±2.33 |
Oil |
236.2±5.02 |
57.5±2.49 |
21.25 mg/kg NP |
221.5±2.20** |
46.7±3.52** |
42.50 mg/kg NP |
213.1±4.27** |
34.8±2.22** |
** Indicates statistical significant compared to control group at (p < 0.01)
Oxidative stress was found in testes tissue following NP exposure indicated by significant increase in testes MDA concentrations (p < 0.05) and decrease in GSH levels and SOD activities (p < 0.001) (Table 5).
Table 5: Epididymal sperm count, sperm motility and abnormal sperm rate
Parameters |
MDA |
GSH |
SOD |
Control |
76.0±9.9 |
1.65±0.07 |
357±6.9 |
Oil |
87.1±9.4 |
1.64±0.04 |
351±8.1 |
21.25 mg/kg NP |
108.2±8.0* |
1.11±0.03*** |
224±7.9*** |
42.50 mg/kg NP |
117.3±9.9* |
1.16±0.06*** |
220±8.6*** |
*, *** Indicates significant compared to control group at (p < 0.05), (p < 0.001), respectively.
In the present study, the observed deleterious effects on sperm characteristics and testicular tissue may be attributed to peroxidation of unsaturated fatty acids in the plasma membrane that may lead to alteration of membrane characteristics and function.
Applicant's summary and conclusion
- Conclusions:
- The purpose of this study was to investigate the effects of NP on sperm characteristics, fertility index, histopathological and biochemical changes related to oxidative stress in testes. Exposure of 10 adult male mice to high dose of NP (1/4 LD50) for 35 days had effects on some reproductive organs weight and sperm characteristics (count and motility), testicular MDA, GSH, and SOD but did not influence the mating behavior, male fertility or the developed fetuses.
- Executive summary:
In a testicular toxicity study nonylphenol (> 85 %) was administered by i.p. injection to 10 male Swiss mice/dose at dose levels of 0, 21.25, and 42.50 mg/kg bw/day for 35 consecutive days. Males were subsequently mated with untreated females. Control male mice received no treatment.
Exposure to 42.5 mg/kg/d (1/4 LD50) had effects on some reproductive organs weight and sperm characteristics (count and motility), testicular MDA, GSH, and SOD but did not influence the mating behavior, male fertility or the developed fetuses.
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