2,3-Epoxypropyl neodecanoate, oligomeric reaction products with cyclohexane-1,2-dicarboxylic anhydride and propylidenetrimethanol

Endpoint summary

Key value for chemical safety assessment

Effects on fertility

Description of key information

An OECD 422 screening study is available for the submission substance and reports a NOAEL of 1000 mg/kg bw/d.

Link to relevant study records

Reference

Endpoint:

screening for reproductive / developmental toxicity

Type of information:

experimental study

Adequacy of study:

key study

Study period:

10 November 2017 - 6 January 2018 (in-life)

Reliability:

1 (reliable without restriction)

Rationale for reliability incl. deficiencies:

guideline study

Reason / purpose for cross-reference:

reference to same study

Qualifier:

according to guideline

Guideline:

OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)

Version / remarks:

July 29, 2016

Deviations:

no

GLP compliance:

yes

Limit test:

no

Specific details on test material used for the study:

Epoxypropyl neodecanoate, oligomeric reaction products with cyclohexane-1,2-dicarboxylic anhydride
and propylidenetrimethanol (HP1365)
Stability: 12 days ambient and refrigerated (2 to 8¿C), as established in MPI Research Study 2622-00
1
Correction Factor: 1.029 (purity 97.2%)
Storage Conditions: Room temperature
Date Received: June 21, 2017
Received From: PPG Industries Italia S.r.l. Quattordio, Italy
Label Identification: Epoxypropyl Neodecanoate, Oligomeric Reaction Products with Cyclohexane-1,2
Dicarboxylic Anhydride and Propylidenetrimethanol
Lot Number: CVR 83297
Physical Characteristics: Clear, yellow gel
Expiration Date: December 27, 2018
Storage: Controlled room temperature, protected from light
TMC Number: 1705BB

Species:

rat

Strain:

Sprague-Dawley

Details on species / strain selection:

Rat: CD®[Crl:CD®(SD)]. The rat is the usual rodent model used for evaluating the toxicity of various classes of chemicals and for which there is a large historical database.

Sex:

male/female

Details on test animals or test system and environmental conditions:

TEST ANIMALS
- Source: Charles River Laboratories
- Females (if applicable) nulliparous and non-pregnant: yes
- Age at study initiation: 8 weeks
- Weight at study initiation: 267-307 g (M), 174-220 g (F)
- Fasting period before study: No
- Housing: Individually, except during pairing, near parturition, and during lactation.
- Diet: ad libitum
- Water: ad libitum
- Acclimation period: 2 weeks

DETAILS OF FOOD AND WATER QUALITY:
Block Lab Diet (Certified Rodent Diet #5002, PMI Nutrition International, Inc.) was available ad libitum, except during designated periods (overnight prior to clinical pathology blood sample collection intervals). The lot number from each diet lot used for this study was recorded. Certification analysis of each diet lot was performed by the manufacturer. Tap water was available ad libitum via an automatic watering system. The water supply is monitored for specified contaminants at periodic intervals according to SOP. The results of food and water analyses are retained in the Archives. The Study Director was not aware of any potential contaminants likely to be present in the diet or water that would have interfered with the results of the study. Therefore, no analyses other than those stated above were conducted.

ENVIRONMENTAL CONDITIONS
- Temperature (°C):
20-26
- Humidity (%): 30-70
- Photoperiod (hrs dark / hrs light):
12/12

IN-LIFE DATES: From: 10 November 2017 To: 6 January 2018

Route of administration:

oral: gavage

Details on exposure:

Animals were dosed daily by gavage at dose levels of 0, 100, 300, and 1000 mg/kg bw/d and a dose volume of 10 mL/kg bw. The vehicle and test article formulations were continually stirred prior to and throughout dose administration. Individual doses were based on the most recent body weights.

Details on mating procedure:

On Day 15, each Repro/Dev Tox female was housed in the cage of a male from the same treatment group. Positive evidence of copulation was established by daily inspection for a copulatory plug in the vagina and/or the presence of sperm in the vaginal lavage. The day on which positive evidence of copulation was observed was considered GD 0. After evidence of mating was observed, the female was returned to an individual cage for the remainder of the study. The maximum pairing period was 14 days, at the end of which any females with no confirmed evidence of mating were returned to individual cages until scheduled euthanasia. 28-Day Tox females and animals designated for the recovery period were not cohabitated.

Analytical verification of doses or concentrations:

yes

Details on analytical verification of doses or concentrations:

Samples were taken from dosing preparations for the assessment of achieved concentration and homogeneity. Samples were collected while the preparations are being stirred. All analytical work was conducted by MPI Research, Mattawan, MI using an analytical method developed by MPI Research and validated under MPI Research Study Number 2622-001.

Duration of treatment / exposure:

The males were dosed for 2 weeks prior to mating and through the mating period for a total of 28 days. Females used for reproductive/developmental toxicity assessment were dosed for 2 week prior to mating and through the mating period. Females that delivered and retained litters were dosed to LD13. Females that did not deliver and did not have evidence of mating were dosed for 24 days after the cohabitation period ended. Females used for toxicity assessment were dosed for 28 days. The recovery males and recovery females, which were not cohabitated, were dosed for 28 days and then remained on study for a 14-day recovery period.

Frequency of treatment:

Daily

Details on study schedule:

Daily, with the exception of recovery animals

Dose / conc.:

0 mg/kg bw/day (actual dose received)

Remarks:

Vehicle (PEG 400) control

Dose / conc.:

100 mg/kg bw/day (actual dose received)

Dose / conc.:

300 mg/kg bw/day (actual dose received)

Dose / conc.:

1 000 mg/kg bw/day (nominal)

No. of animals per sex per dose:

10/sex (reproductive/developmental toxicity assessment)
10/sex (toxicity assessment)
5/sex (recovery groups)

Control animals:

yes, concurrent vehicle

Details on study design:

The dose levels were selected on the basis of available data from a 14-day oral toxicity study in rats (MPI Research Study Number 2622-0037). No adverse findings were observed on body weights, food consumption, and macroscopic findings at dose levels ¿1000 mg/kg bw/d in the 14-day study. The only clinical observation was piloerection in a few animals in each dose group (100, 300, and 1000 mg/kg bw/d) on the last day of testing. The high dose level for this study was selected in accordance with the maximum dose level recommended in the testing guidance and the lower doses for determination of a dose-response. 10 rats/sex/group were assigned to the reproductive/developmental toxicity assessment. Males were treated for 14 days prior to mating and during mating, for at least 28 days. Females were treated for 14 days prior to mating, during mating, gestation and lactation (to LD13). 10 rats/sex/group were assigned to the toxicity assessment and were treated for 28 days. An additional 5 rats/sex (control and high dose groups) were treated for 28 days followed by a 14-day recovery period.

Positive control:

Not required for this study type.

Parental animals: Observations and examinations:

CAGE SIDE OBSERVATIONS: Yes
- Time schedule: at least twice daily. All animals were observed for morbidity, mortality, injury, and the availability of food and water. General clinical observations (health condition including behavioural changes and signs of toxicity) were made daily post-dosing.

DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Pre-test and weekly during the study, post-dosing. Observations included, but were not limited to, evaluation of the skin, fur, eyes, ears, nose, oral cavity, thorax, abdomen, external genitalia, limbs and feet, as well as evaluation of respiration.

BODY WEIGHT: Yes
- Time schedule for examinations: Males (weekly and on FOB and locomotor activity days). Repro/Dev Tox females: Weekly (during oestrous evaluations and prior to mating), GD 0, 7, 14, and 20; PND 0 and 4, 7, and 13. Body weight change was calculated for the males and females between each weighing interval and over the entire premating and recovery period and for the Repro/Dev Tox females on GD 0-7, 7-14, 14-20, 0-20 and PND 0-4, 4-7, 7-13 and 0-13.

FOOD CONSUMPTION: Yes
Males and 28-Day Tox Females: Weekly
Repro/Dev Tox Females: Weekly (during oestrous evaluations and prior to mating), GD 0, 7, 14, and 20; PND 0, 4, 7, and 13.
Recovery animals: Weekly
Food consumption was not recorded during mating as animals were cohoused.

WATER CONSUMPTION: No

OPHTHALMOSCOPIC EXAMINATION: No

HAEMATOLOGY: Yes (overnight fasted)
All males, 28-Day Tox females and recovery animals (Day 29 and prior to recovery necropsy). Prothrombin time, Activated partial thromboplastin time, fibrinogen; leukocyte count (total and absolute differential), erythrocyte count, haemoglobin, haematocrit, mean corpuscular hemoglobin, mean corpuscular volume, mean corpuscular hemoglobin concentration (calculated), absolute reticulocytes, platelet count, RDW. Blood smears were preserved and stained for possible future evaluation.

CLINICAL CHEMISTRY: Yes (overnight fasted)
All males, 28-Day Tox females and recovery animals (Day 29 and prior to recovery necropsy). Alkaline phosphatase, total bilirubin (with direct bilirubin if total bilirubin exceeds 1 mg/dL), aspartate aminotransferase, alanine aminotransferase, urea nitrogen, creatinine, total protein, albumin, globulin and A/G (albumin/globulin) ratio (calculated), glucose, total cholesterol, triglycerides, electrolytes (sodium, potassium, chloride), calcium, phosphorus, bile acids. Additionally, blood was collected from all Repro/Dev Tox females delivering a litter and all males at necropsy for TSH and T4 hormone analysis.

URINALYSIS: No

NEUROBEHAVIOURAL EXAMINATION: No

IMMUNOLOGY: No

Oestrous cyclicity (parental animals):

All P females pre-exposure for 2 weeks (selection of only normal cycling females to continue on study), during the 2-week pre-mating dosing period, 14-day cohabitation period until evidence of copulation was detected, and at terminal necropsy.

Sperm parameters (parental animals):

Not investigated

Litter observations:

Toward the end of the gestation period, females were examined twice daily for signs of parturition. The mated females were allowed to give birth (F1). Any female dying during parturition was subjected to gross necropsy, The duration of gestation was calculated, and any difficulties occurring at parturition recorded. The day on which all pups were delivered was designated LD0. The litters were examined as soon as possible after delivery. The following parameters were recorded for each litter. Litter size (total number live born pups, stillborn pups and partially cannibalized pups); Number of stillborn pups; Number of live born pups; Number of pups per sex; Individual pup body weights; Gross abnormalities of the pups. Litters were culled on LD4 to 8 pups (4/sex where possible). Blood was collected for TSH and T4 from at least two pups per litter (pooled) on LD4.

Litters weere housed with their dams to LD13. The dams and litters were observed daily for survival and behavioural alterations in nesting and nursing, and the presence of dead pups recorded. Pups were individually weighed and examined externally on LD0, 4, 7, and 13. The dam and litter remained together until LD 13. Anogenital distance was recorded for all pups on LD4 (post-cull) and the number of nipples counted on male pups on PND 12.

Postmortem examinations (parental animals):

Gross necropsy was performed all surviving males and all 28-day Tox females. For the Repro/Dev Tox females, gross necropsy was performed and the number of implantation scars recorded. The uteri from non-gravid females were stained with ammonium sulphide for the detection of implantation sites. Weights of the adrenals, brain, epididymides, heart, kidneys, liver, lungs, ovaries, prostate, seminal vesicles, spleen, testes, thymus, thyroid and uterus were recorded.

Postmortem examinations (offspring):

F1 pups will be euthanised on LD 4 were externally examined. Blood samples (pooled from at least 2 pups per litter) for T4 and TSH were collected. Any abnormalities were recorded and the carcasses discarded. The thyroid was collected from 1 F1 pup/sex sacrificed on LD 13. All F1 pups were externally examined. Any abnormalities were recorded, and the carcasses will be discarded. If a skeletal anomaly was suspected, the pups were eviscerated, cleared, and stained with Alizarin Red S and examined using Dawson's technique. The thyroid gland was collected from
one pup/sex/litter and saved in 10% neutral buffered formalin for possible histopathological evaluation.

Statistics:

Raw data were tabulated within each time interval, and the mean and standard deviation and/or incidence counts (categorical variables) calculated for each endpoint by sex and group. For each endpoint, treatment groups were compared to the control group. Data for some endpoints, as indicated, were transformed by either a log or rank transformation prior to conducting the specified analysis. All analyses were two-tailed for significance levels of 5% and 1%. All means were presented with standard deviations. All statistical tests were performed by a computer.

Group Pair-wise Comparison (General ANOVA)
Endpoints: Parental In-life Data, Body Weights and Body Weight Change-Males, Premating and Gestation Body Weight and Body Weight Change-Females, Premating Food Consumption-Males and Females, Gestation Food Consumption, Postmating Food Consumption-Males, Haematology (except leukocyte counts), Coagulation, Clinical Chemistry, FOB, Lactation Body Weights (P), Lactation Body Weight Change (P), Lactation Food Consumption (P), Fertility Indices, Copulatory Interval, Gestation Length (P), Litter Size, Viable Pups, Stillborn Pups, Pathology, Organ Weights (Absolute Weights, Relative to Body and Brain Weights).

Generalized Linear Model:
Locomotor Activity (Continuous), Basic Movements, Fine Movements, Rearing, Distance.

Fisher¿s Exact Test with Stepdown Sidak Adjustment:
Male Fertility Index, Female Fertility Index, Female Mating Index, Male Mating Index, Female Fecundity Index, Male Fecundity Index, Gestation Index.

Arcsin-Square Root Transformation:
Pup Sex Ratio (% viable males/litter), Stillborn Index, Pup Survival (Days 0-4 pre-cull and 4-post-cull-Day 13)

Exact Mantel-Haenszel Test with Stepdown Sidak Adjustment:
Categorical FOB data

Covariate Analysis:
Pup Weights

Reproductive indices:

Male Fertility Index
Female Fertility Index
Female Mating Index
Male Mating Index
Female Fecundity Index
Male Fecundity Index
Gestation Index

Offspring viability indices:

Viability Index
Survival Index

Clinical signs:

effects observed, treatment-related

Description (incidence and severity):

No adverse test article-related effects were noted on general clinical observations in females at any of the dose levels evaluated. There were observations of salivation in the 100, 300, 1000 mg/kg bw/d dose groups (1 of 10, 1 of 9, and 1 of 7 females, respectively) during the mating and gestation periods. Other observations noted during the course of the study were not considered treatmnet-related due to a low incidence, concurrent finding in control animals, and/or expected findings for rats of this strain.

No adverse test article-related effects were noted on detailed clinical observations in females at any of the dose levels evaluated. In the females, there were observations of salivation in the 100 and 1000 mg/kg bw/d dose groups (1 of 10 and 3 of 10 females, respectively) during the premating period and in the 300 mg/kg/bw/d group (1 of 9 females) during the lactation period. While the increased observation of salivation may be treatment-related, there was no impact on the overall health of the animals, and therefore not considered adverse. Other observations noted during the course of the study were not considered treatment-related due to a low incidence, concurrent finding in control animals, and/or expected findings for rats of this strain.

Dermal irritation (if dermal study):

not examined

Mortality:

mortality observed, non-treatment-related

Description (incidence):

One control female was found dead on Study Day 36. There were no clinical observations, body weight loss, or decrease in caged food consumption for this animal prior to being found dead. All other animals in the Repro/Dev Tox phase survived to the scheduled study termination.

Body weight and weight changes:

no effects observed

Description (incidence and severity):

No treatment-related effects were observed on mean body weight or body weight change in the females at any of the dose levels evaluated. The few statistically significant differences observed in these data between the control and treated groups occurred sporadically and often due to the directions of the change were considered incidental and unrelated to treatment.

Food consumption and compound intake (if feeding study):

no effects observed

Description (incidence and severity):

No treatment-related effects were observed on caged food consumption in the females at any of the dose levels evaluated. The few statistically significany increases observed in these data between the control and treated groups occurred sporadically, lacked dose-responsiveness, and were considered incidental and unrelated to treatment.

Food efficiency:

not examined

Water consumption and compound intake (if drinking water study):

not examined

Ophthalmological findings:

not examined

Haematological findings:

no effects observed

Clinical biochemistry findings:

no effects observed

Urinalysis findings:

not examined

Behaviour (functional findings):

not examined

Description (incidence and severity):

FOB and motor assessment were assessed in this study in animals assigned to the toxicity group and are reported separately.

Immunological findings:

not examined

Organ weight findings including organ / body weight ratios:

no effects observed

Histopathological findings: non-neoplastic:

not examined

Histopathological findings: neoplastic:

not examined

Other effects:

no effects observed

Reproductive function: oestrous cycle:

effects observed, treatment-related

Description (incidence and severity):

No treatment-related effects were observed on mean cycle length in the Repro/Dev Tox females at any of the dose levels evacuated. At 300 and 1000 mg/kg bw/d there was a significant decrease in number of cycles compared to controls (-25 and -29%, respectively). While this decrease may be treatment-related, without effects on the reproductive and fertility parameters it was not considered adverse.

Reproductive function: sperm measures:

not examined

Reproductive performance:

no effects observed

Description (incidence and severity):

No effect of treatment was observed on mating, fertility or fecundity indices in males or females. These indices in each of the treated groups were comparable to control values. Likewise, the mean Copulatory Interval (mean days-to-mating) in the test article-treated groups which ranged from 2.6 to 3.9 days was comparable to the mean of 2.9 days in the control group.No test article-related effect was observed on parturition data in the P females at any of the dose levels evaluated. Pregnancy rates for the P females were 80, 100, 90, and 80%, providing 7, 10, 9, and 8 litters with viable pups in the control, 100, 300, and 1000 mg/kg bw/d groups, respectively. Parturition parameters (i.e., incidence of animals with stillborn pups, mean number of pups at birth [liveborn, stillborn and total], Gestation Index, Stillborn Index, and mean number of uterine implantation scars at necropsy) in the treated groups were comparable to controls.

One control female died: there was no treatment-related mortality. Clinical signs attributable to treatment were limited to post-dosing salivation in all treated groups of females. Bodyweights and food consumption were unaffected by treatment. At 300 and 1000 mg/kg bw/d there was a significant decrease in number of cycles compared to controls (-25 and -29%, respectively); findings at the highest dose level are attributable at least in part to one dam with an oestrus cycle length of 11 days. While this decrease may be treatment-related, without effects on the reproductive and fertility parameters it was not considered adverse. No effects of treatment were seen on measures of fertility.

Key result

Dose descriptor:

NOAEL

Effect level:

1 000 mg/kg bw/day (actual dose received)

Based on:

test mat.

Sex:

male/female

Remarks on result:

not determinable due to absence of adverse toxic effects

Key result

Critical effects observed:

no

Clinical signs:

no effects observed

Description (incidence and severity):

No effect of treatment was observed from F1 pup detailed clinical observations at any of the dose levels evaluated. The few findings observed in the pups from the treated groups occurred at low incidence or with similar frequency to controls and were considered unrelated to treatment.

Dermal irritation (if dermal study):

not examined

Mortality / viability:

no mortality observed

Description (incidence and severity):

No effect of treatment on F1 pup survival over LD 0-4 or LD 4-13 was observed in the treated groups in comparison to controls. Mean pup survival LD 0-4 ranged from 95.37% to 99.31% in the treated groups and was comparable to controls at 97.62%. Mean pup survival was 100% in all groups over LD 4-13. Litter size in the treated groups on LD 4 pre- and post-cull, and at LD 13 was comparable to controls.

Body weight and weight changes:

no effects observed

Description (incidence and severity):

No treatment-related effect was observed on F1 pup body weights (male, female, and male and female combined) at any of the dose levels evaluated.

Food consumption and compound intake (if feeding study):

not examined

Food efficiency:

not examined

Water consumption and compound intake (if drinking water study):

not examined

Ophthalmological findings:

not examined

Haematological findings:

not examined

Clinical biochemistry findings:

effects observed, treatment-related

Description (incidence and severity):

Moderate increases in serum Thyroid Stimulating Hormone (TSH) concentrations on Lactation Day 4 were seen in pups from dams at 300 and 1000 mg/kg bw/d. There were no associated alterations in serum thyroxine (T4) concentrations or microscopic findings in the thyroid gland, and increases in TSH concentrations were not considered to be adverse.

Urinalysis findings:

not examined

Sexual maturation:

not examined

Organ weight findings including organ / body weight ratios:

not examined

Gross pathological findings:

no effects observed

Description (incidence and severity):

No effects were observed from macroscopi examination of stillborn pups, pups dying on study, LD 4 culled pups, or LD 13 pups.

Histopathological findings:

not examined

Other effects:

no effects observed

Description (incidence and severity):

No treatment-related effect was observed on F1 pup anogenital distance or nipple count at any of the dose levels evaluated.

Behaviour (functional findings):

not examined

Developmental immunotoxicity:

not examined

Pup viability and growth were unaffected by treatment at any dose level. Moderate increases in serum Thyroid Stimulating Hormone (TSH) concentrations on Lactation Day 4 were seen in pups from dams at 300 and 1000 mg/kg bw/d. There were no associated alterations in serum thyroxine (T4) concentrations or microscopic findings in the thyroid gland, and increases in TSH concentrations were not considered to be adverse.

Key result

Dose descriptor:

NOAEL

Generation:

F1

Effect level:

1 000 mg/kg bw/day (nominal)

Based on:

test mat.

Sex:

male/female

Remarks on result:

not determinable due to absence of adverse toxic effects

Key result

Critical effects observed:

no

Key result

Reproductive effects observed:

no

Summary of fertility parameters

	0	100	300	1000
Males paired (#)	9	10	10	10
Males mated (#)	8	10	9	8
Males impregnating females (#)	8	10	9	8
Male mating index	88.9	100	90.0	80.0
Male fertility index	88.9	100	90.0	80.0
Male fecundity index	100	100	100	100
Females paired (#)	10	10	10	10
Females mated (#)	8	10	9	8
Females pregnant (#)	8	10	9	8
Female mating index	80.0	100	90.0	80.0
Female fertility index	80.0	100	90.0	80.0
Female fecundity index	100	100	100	100

Summary of findings in dams

	F
	0	100	300	1000
Mortality	1	-	-	-
Salivation	-	1	1	3
Bodyweight (g) pre-mating	241.4	234.0	239.7	234.2
Bodyweight (g) GD20	414.0	401.9	395.0	383.6
Bodyweight (g) LD20	351.0	338.3	336.7	339.5
Weight gain (g) pre-mating	41.2	37.2	42.0	35.5
Weight gain (g) gestation	154.9	158.7	148.1	148.6
Weight gain (g) lactation	30.9	32.8	31.3	41.1
Oestrus cycle length (d)	4.6	4.7	4.6	5.6
[No. cycles]	2.8	2.4	2.1*	2.0*

*significantly different to controls (p<0.05)

Summary of litter parameters

	0	100	300	1000
Females on study (#)	10	10	10	10
Females pregnant (#)	8	10	9	8
Litters (#)	7	10	9	8
Gestation length (d)	21.4	21.6	21.5	21.8
Litter size (#)	15.71	14.40	14.56	13.50
Stillborn (#)	0.0	0.1	0.0	0.1

Summary of offspring viability and growth

	0	100	300	1000
Live pups PND0 (#)	15.7	14.3	14.6	13.4
Live pups PND4 (#) pre-cull	15.3	13.6	14.4	13.1
Live pups PND4 (#) post-cull	8.0	8.0	8.0	8.0
Live pups PND7 (#)	8.0	8.0	8.0	8.0
Live pups PND13 (#)	8.0	8.0	8.0	8.0
Viability index (%)	97.6	95.4	99.3	98.0
PND 4-13 Survival index (%)	100	100	100	100
Pup weight (g) PND0	6.51	6.45	6.36	6.63
Pup weight (g) PND4	9.92	9.79	10.08	10.00
Pup weight (g) PND7	15.94	16.24	16.17	16.35
Pup weight (g) PND13	31.07	30.17	31.20	31.41
AGD (mm) PND4	3.286	3.475	3.278	4.094

Summary of thyroid hormone measurements

		0	100	300	1000
T4 (µg/dL)	Pups PND4	2.701	2.715	3.003	3.116
	Dams LD13	3.871	4.237	4.042	4.073
	Pups LD13	7.674	7.898	8.331	8.095
	Males Day 29	4.597	5.181	5.328	5.533
TSH (ng/dL)	Pups PND4	1.687	2.603	4.329	8.664
	Dams LD13	6.774	8.300	5.739	7.793
	Pups LD13	4.921	5.554	5.501	3.890
	Males Day 29	2.896	3.292	3.354	4.302

Conclusions:

In the absence of any findings of toxicological significance, a parental NOAEL of 1000 mg/kg bw/d can be determined for this study. A reproductive NOAEL of 1000 mg/kg bw/d can also be determined in the absence of any effects on fertility or development.

Executive summary:

This OECD 422 screening study was conducted to evaluate for possible adverse effects of the submission substance (epoxypropyl neodecanoate, oligomeric reaction products with cyclohexane-1,2-dicarboxylic anhydride and propylidenetrimethanol) following repeated dosing to male and female rats, including systemic toxicity, neurotoxic potential, reproductive performance (gonadal function, mating behavior, conception, development of the conceptus, and parturition), and F1 offspring growth and maturation up through LD 13. No effects on treated males and females were observed on survival, clinical observations, body weights and body weight change, food consumption, oestrous cycle parameters, reproductive performance (mating, fertility, and fecundity), behavioural evaluations (functional observational battery and locomotor activity), clinical pathology parameters, organ weights, macroscopic observations, and microscopic observations. No effects of treatment were observed on F1 survival, clinical observations, body weights, and macroscopic findings. Based on these findings, 1000 mg/kg bw/d, the highest dose level evaluated, was considered to be the NOAEL.

Effect on fertility: via oral route

Endpoint conclusion:

no adverse effect observed

Dose descriptor:

NOAEL

1 000 mg/kg bw/day

Study duration:

subacute

Species:

rat

Quality of whole database:

A modern, guideline- and GLP-compliant OECD 422 screening study is avaialble for the submission substance.

Effect on fertility: via inhalation route

Endpoint conclusion:

no study available

Effect on fertility: via dermal route

Endpoint conclusion:

no study available

Additional information

No adverse effects of treatment were seen on parental toxicity, fertility or development in an OECD 422 study perfomred with the submission substance at dose levels of up to 1000 mg/kg bw/d. Post-dosing salivation observed in a small number of dams from all treated groups is likely to be treatment-related but is not considered to represent an adverse effect. Bodyweights and food consumption were unaffected by treatment.  At 300 and 1000 mg/kg bw/d there was a significant decrease in number of cycles compared to controls (-25 and -29%, respectively); findings at the highest dose level are attributable at least in part to one dam with an oestrus cycle length of 11 days.  While this decrease may be treatment-related, without effects on the reproductive and fertility parameters it was not considered adverse.  No effects of treatment were seen on measures of fertility. Pup viability and growth were unaffected by treatment at any dose level.  Moderate increases in serum Thyroid Stimulating Hormone (TSH) concentrations on Lactation Day 4 were seen in pups from dams at 300 and 1000 mg/kg bw/d.  There were no associated alterations in serum thyroxine (T4) concentrations or microscopic findings in the thyroid gland, and increases in TSH concentrations were not considered to be adverse.

Effects on developmental toxicity

Description of key information

An OECD 422 screening study is available for the submission substance and reports a NOAEL of 1000 mg/kg bw/d; there are no additional data on developmental toxicity.

Effect on developmental toxicity: via oral route

Endpoint conclusion:

no adverse effect observed

Dose descriptor:

NOAEL

1 000 mg/kg bw/day

Study duration:

subacute

Species:

rat

Quality of whole database:

A modern, guideline- and GLP-compliant OECD 422 screening study is avaialble for the submission substance.

Effect on developmental toxicity: via inhalation route

Endpoint conclusion:

no study available

Effect on developmental toxicity: via dermal route

Endpoint conclusion:

no study available

Additional information

An OECD 422 screening study is available for the submission substance and reports a NOAEL of 1000 mg/kg bw/d; there are no additional data on developmental toxicity.

Justification for classification or non-classification

A screening study with the submission substance reports a NOAEL of 1000 mg/kg bw/d; no additional data are available. In the absence of any indication of reproductive or developmental toxicity, no classification for reproductive toxicity is proposed under CLP.