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Diss Factsheets

Administrative data

Description of key information

Key value for chemical safety assessment

Toxic effect type:
dose-dependent

Repeated dose toxicity: via oral route - systemic effects

Link to relevant study records

Referenceopen allclose all

Endpoint:
short-term repeated dose toxicity: oral
Type of information:
experimental study
Adequacy of study:
supporting study
Study period:
1983
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
comparable to guideline study
Remarks:
Well conducted and comparable to guideline study, no information on GLP status
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 407 (Repeated Dose 28-Day Oral Toxicity Study in Rodents)
Deviations:
no
GLP compliance:
no
Limit test:
no
Species:
rat
Strain:
Wistar
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Mus-Rattus, Brunntal, Germany
- Strain: Wistar rat, MuRa Han 67 SPF
- Age at study initiation: between 6-7 weeks
- Weight at study initiation: 109 (f) - 114 (m) g
- Housing: plastic cages, 3 males and 5 females/cage
- Diet (e.g. ad libitum): ad libitum (Altromin Ratdiet No. 1424 DK, Altromin GmbH, Lage, Germany)
- Water (e.g. ad libitum): ad libitum (tap water)
- Acclimation period: 6 d

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19-22
- Humidity (%): 60-80
- Air changes (per hr): 11
- Photoperiod (hrs dark / hrs light): 12/12
Route of administration:
oral: gavage
Vehicle:
olive oil
Details on oral exposure:
Doses were adapted weekly to the body weight; application volume - 5 mL/kg bw
Analytical verification of doses or concentrations:
no
Duration of treatment / exposure:
28 d
Frequency of treatment:
Daily once, 5 times/wk
Dose / conc.:
0 mg/kg bw/day (actual dose received)
Dose / conc.:
70 mg/kg bw/day (actual dose received)
Remarks:
Days 1-28
Dose / conc.:
250 mg/kg bw/day (actual dose received)
Remarks:
Days 1-28
Dose / conc.:
750 mg/kg bw/day (actual dose received)
Remarks:
Days 1-14
Dose / conc.:
1 500 mg/kg bw/day (actual dose received)
Remarks:
Days 15-28
No. of animals per sex per dose:
10/sex/dose for main study; 5/sex/dose for 4 months recovery period


Control animals:
yes, concurrent no treatment
Details on study design:
According to standard procedure
Observations and examinations performed and frequency:
CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily

DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: end of study

BODY WEIGHT: Yes
- Time schedule for examinations: weekly

HAEMATOLOGY: Yes
- Time schedule for collection of blood: end of study
- Anaesthetic used for blood collection: Yes (ether)
- How many animals: 10 per dose and sex
- Parameters checked: Hematocrit, erythrocytes, leukocytes, hemoglobin, thrombocytes, mean corpuscular volume, white blood cell differential

CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: end of study
- How many animals: 10 per sex and dose
- Parameters checked: GPT, GOT, AP, glucose, urea, total protein, calcium, phosphate, cholesterol

URINALYSIS: Yes
- Time schedule for collection of urine: end of study
- Metabolism cages used for collection of urine: No
- Parameters checked: urea, creatinine, sodium, potassium, glucose, calcium, AP

NEUROBEHAVIOURAL EXAMINATION: No

Other: Groups of 5 male and 5 female rats kept for an additional 4 month recovery period.
Sacrifice and pathology:
GROSS PATHOLOGY: Yes
the following tissues/organs were examined:
adrenal gland
aorta thoracica
brain (cornu ammonis)
coagulating gland with seminal vesicle
epididymis
eye with optic nerve
heart
intestine, large
intestine, small
kidney
liver
lungs
lymph node (cervical)
lymph node (mesenteric)
mucles
oesophagus
ovary
pancreas
prostate
salivary glands (mandibular,
parotid and sublingual gland)
skin
spleen
stomach
testicle
thymus
thyroid (incl. parathyroids)
tongue
trachea (incl. larynx)
urinary bladder
uterus (incl. cervix and oviducts)


HISTOPATHOLOGY: Yes
see gross pathology
Statistics:
't' test used for statistical analysis of all parameters except organ weight (U-test)


Clinical signs:
no effects observed
Mortality:
no mortality observed
Description (incidence):
The doses up to 1500 mg/kg bw/day were tolerated by all animals without lethality.
Body weight and weight changes:
no effects observed
Description (incidence and severity):
The body weight gain and total increase of body weights did not differ from the control group.
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 examined
Haematological findings:
no effects observed
Clinical biochemistry findings:
effects observed, treatment-related
Description (incidence and severity):
The biochemical parameters calcium, blood sugar, urea, creatinine, cholesterine, GGT, GOT, GPT and LDH did not show any critical signs. Only slight shifts which were not dose-dependent could be observed. These signs were considered as not substance depending.
Urinalysis findings:
no effects observed
Behaviour (functional findings):
not examined
Organ weight findings including organ / body weight ratios:
effects observed, treatment-related
Description (incidence and severity):
Absolute and relative organ weights showed no significant changes in the substance groups compared to the control group, except the organ weight of the liver which is slightly increased for the males of group 4 (750/1500 mg/kg bw) and increased adrenal glands weight in high dose females. This result is considered of no relevance.
Gross pathological findings:
no effects observed
Description (incidence and severity):
The pathological and histological evaluation did not show significant compound related gross or microscocopic organ injury of liver, kidneys, adrenals, heart, lung, spleen and gonads; dose dependent reversible local findings were restricted to the fore stomach mucosa (important hyperplasia and ulcerations, in some cases also hyper- and parakeratosis of the forestomach of males and females at the high dose. Similar effects but less intense at the medium and low doses).
Histopathological findings: non-neoplastic:
no effects observed
Description (incidence and severity):
The pathological and histological evaluation did not show significant compound related gross or microscocopic organ injury of liver, kidneys, adrenals, heart, lung, spleen and gonads; dose dependent reversible local findings were restricted to the fore stomach mucosa (important hyperplasia and ulcerations, in some cases also hyper- and parakeratosis of the forestomach of males and females at the high dose. Similar effects but less intense at the medium and low doses).
Histopathological findings: neoplastic:
no effects observed
Key result
Dose descriptor:
NOAEL
Effect level:
> 750 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
other: No biologically relevant treatment-related effects observed on any of the parameters recorded at any dose, also test animals treated with 1500 mg/kg bw (Days 15-28) showed no adverse effect
Key result
Critical effects observed:
no
Conclusions:
Under the study conditions, the 28 d NOAEL to rats was considered to be >750 mg/kg bw/day.
Executive summary:

A study was conducted to evaluate the repeated dose oral toxicity of the test substance, C12-18 and C18-unsatd. DEA, according to design based on OECD guideline 407. Groups of 10 male and 10 female Wistar rats were orally gavaged with the substance diluted in olive oil, 5 d/week for 28 d at doses of 0, 70, 250, 750 (Days 1-14) and 1500 (Days 15-28) mg/kg bw/d. Clinical signs, bodyweight, haematology, clinical chemistry, urinalysis, gross and microscopic pathology were recorded. Additional groups of 5 male and 5 female rats were kept for a 4 month recovery period. No treatment-related adverse effects were observed at any of the doses. Changes in the forestomach at some doses including controls were attributed to the use of olive oil and found to be reversible after end of exposure. Under the study conditions, the 28 d NOAEL to rats was considered to be >750 mg/kg bw/day (Potokar, 1983).

Endpoint:
short-term repeated dose toxicity: oral
Remarks:
Combined repeated dose toxicity study with the reproduction / developmental toxicity screening
Type of information:
read-across based on grouping of substances (category approach)
Adequacy of study:
key study
Study period:
From March 10, 2021 to February 4, 2022
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study
Justification for type of information:
Refer to section 13 of IUCLID for details on the category justification.
Reason / purpose for cross-reference:
read-across source
Qualifier:
according to guideline
Guideline:
OECD Guideline 422 (Combined Repeated Dose Toxicity Study with the Reproduction / Developmental Toxicity Screening Test)
Version / remarks:
adopted on 29 July 2016
Deviations:
yes
Remarks:
Females and males were supplied in the weight range of 178-235 and 201-222 g and not 175-200 and 200-225 g. Motor activity measurements were carried out Week 5 and not Week 4, as indicated in the Study Protocol. These deviations had no impact on the study
GLP compliance:
yes (incl. QA statement)
Limit test:
no
Species:
rat
Strain:
Sprague-Dawley
Remarks:
Hsd: Sprague Dawley SD rats
Details on species / strain selection:
The Sprague Dawley rat is the species and strain of choice because it is accepted by many regulatory authorities and there is ample experience and background data on this species and strain.
Sex:
male/female
Details on test animals or test system and environmental conditions:
- Animal supply and acclimatization:
A total of 102 Hsd: Sprague Dawley SD rats (45 males and 57 virgin females), 7 to 8 weeks old and weighing 200 to 225 g for males and 175 to 200 g for females, were ordered from and supplied by Charles River Italia S.p.A., Calco (Lecco), Italy. After arrival, the weight range for each sex was determined and the animals were temporarily identified within the cage by means of a coloured mark on the tail. A health check was then performed by a veterinarian. An acclimatisation period of approximately 4 weeks was allowed before the start of treatment, during which time the health status of the animals was assessed by thorough observations.

- Animal husbandry:
The animals were housed in a limited access rodent facility. Animal room controls were set to maintain temperature and relative humidity at 22°C±2°C and 55%±15%, respectively; actual conditions were monitored, recorded and the records retained. There were approximately 15 to 20 air changes per hour and the rooms were lit by artificial light for 12 hours each day. From arrival to mating, animals were housed up to 5 of one sex to a cage, in polysulfone solid bottomed cages measuring 59.5×38×20 cm (Tecniplast Gazzada S.a.r.l., Buguggiate, Varese). Nesting material was provided inside suitable bedding bags and changed at least twice a week. During mating, animals were housed one male to one female in clear polysulfone cages measuring 42.5×26.6×18.5 cm with a stainless steel mesh lid and floor (Tecniplast Gazzada S.a.r.l., Buguggiate, Varese). Each cage tray held absorbent material which was inspected and changed daily. After mating, the males were re-caged as they were before mating. The females were transferred to individual solid bottomed cages for the gestation period, birth and lactation (measuring 42.5×26.6×18.5 cm). Nesting material was provided inside suitable bedding bags. In addition, suitable nesting material (Scobis 0 Mucedola) was provided as necessary and changed at least 2 times a week. Drinking water was supplied ad libitum to each cage via water bottles, except in the case of urinalysis investigations. A commercially available laboratory rodent diet (4 RF 21, Mucedola S.r.l., Via G. Galilei, 4, 20019 Settimo Milanese (MI), Italy) was offered ad libitum throughout the study. There was no information available to indicate that any non-nutrient substance likely to influence the effect of the test item was present in the drinking water or the diet. Records of analyses of water and diet are kept on file at ERBC. Dated and signed records of activities relating to the day to day running and maintenance of the study in the animal house were recorded.

- Allocation to groups:
On the day of allocation all animals were weighed. Animals at the extremes of the weight distribution were excluded to leave the required number of animals. Furthermore, female animals that exhibited anomalies in the oestrous cycle were not allocated to the main groups. The rats were allocated to the groups by computerised stratified randomisation to give approximately equal initial group mean body weights. Individuals were uniquely identified within the study by sex, tattoo on the hind feet and ear notch and housed five per sex per cage. The cages were identified by a label and recording the study number, animal numbers and details of treatment. The arrangement of cages in batteries was such that cages from each group were distributed to minimise possible environmental effects and or contamination. Any animal showing signs of ill health during the period between allocation and the start of treatment was subjected to pathological examination as considered appropriate and replaced with a surplus animal selected from the same batch.
Route of administration:
oral: gavage
Details on route of administration:
The test item will be administered orally, by gavage. The oral route has been selected as it is a possible route of exposure of the test substance in man.
Vehicle:
CMC (carboxymethyl cellulose)
Remarks:
0.5% CMC
Details on oral exposure:
The required amount of test substance was suspended in the vehicle. The formulations were prepared weekly or daily (concentrations of 10, 25 and 70 mg/mL), according to stability data from ERBC study No. A4125. Concentrations were calculated and expressed in terms of test substance as supplied. The test substance was administered orally by gavage at a dose volume of 10 mL/kg body weight. Control animals received the vehicle alone at the same dose volume. The dose was administered to each animal on the basis of the most recently recorded body weight and the volume administered was recorded for each animal.
Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
The analytical method was validated in ERBC Study no. A4125 in the range from 10 to 100 mg/mL. Linearity, accuracy and precision were within the limits stated in the validation study (r > 0.99; accuracy 80-120%; precision CV < 10%). In ERBC Study no. A4125, a 48 hour stability at room temperature and a 9 day stabiliy at 2-8°C were verified in the range from 10 to 100mg/mL. According to ERBC SOPs, suspensions were considered to be stable if concentration and homogeneity, after the defined period of storage, were still acceptable (80%-120% for concentration and CV < 10% for homogeneity). The proposed preparation procedure for the test item was checked in the range from 10 to 100mg/mL by chemical analysis (concentration and homogeneity) in ERBC Study no. A4125 to confirm that the method was suitable. Final results for all levels were within the acceptability limits stated in ERBC SOPs for concentration (80-120%) and homogeneity (CV < 10%). Samples of the preparations prepared onWeek 1 and 5 (last week with males and females) were analysed to check the homogeneity and concentration. Results of the analyses were within the acceptability limits stated in ERBC SOPs for suspensions (80-120% for concentration and CV < 10% for homogeneity). Chemical analysis was carried out by the Analytical Chemistry Department. The software used for this activity was Empower® 2 Build No. 2154.
Duration of treatment / exposure:
Males: Animals were dosed once a day, 7 days a week, for 14 days prior to pairing, through the pairing period and thereafter until the day before necropsy or the day before sacrifice, up to a total of 33/34 days for surviving animals. Dose volumes were adjusted once per week for each animal according to the last recorded body weight.

Females: Animals were dosed once a day, 7 days a week, for 14 days prior to pairing and thereafter during pairing, post coitum and post partum periods until Day 13 post partum or the day before sacrifice (for a total of 43 to 63 days). Dose volumes were adjusted once per week for each animal according to the last recorded body weight up to mating. During the gestation and lactation periods, dose volumes were calculated according to the last recorded body weight.
Frequency of treatment:
Once daily, 7 days/weeks
Dose / conc.:
0 mg/kg bw/day (nominal)
Dose / conc.:
100 mg/kg bw/day (nominal)
Dose / conc.:
250 mg/kg bw/day (nominal)
Dose / conc.:
700 mg/kg bw/day (nominal)
No. of animals per sex per dose:
10 rats per sex per dose
Control animals:
yes, concurrent vehicle
Observations and examinations performed and frequency:
- Mortality:
Throughout the study, all animals were checked early in the morning and in the afternoon each working day. At weekends and Public Holidays a similar procedure was followed except that the final check was carried out at approximately mid-day.

- Clinical signs:
Once before commencement of treatment and at least once daily during the study, each animal was observed and any clinical signs was recorded. Observations were performed at the same time interval each day, the interval was selected taking into consideration the presence of post-dose reactions. Observations were performed at the same time interval each day (approximately 5 - 10 minutes and 1.30 - 2 hours post-dose), the interval was selected taking into consideration the presence of post-dose reactions. All observations were recorded for individual animals.

- Clinical Observations (Functional Observation Battery Tests):
Once before commencement of treatment and once a week thereafter, each animal was given a detailed clinical examination (ERBC SOP no. ANI/344). Each animal was removed from the home cage and observed in an open arena. The tests included observation of changes in gait and posture, reactivity to handling, presence of clonic or tonic movements, stereotypies or bizarre behaviour and effects on the autonomic nervous system (e.g. lachrymation, piloerection, pupil size, unusual respiratory pattern). Changes in fur, skin, eyes, mucous membranes, occurrences of secretions and excretions were also recorded. All observations were recorded for individual animals.

- Grip strength and sensory reactivity to stimuli:
Once during the study, towards the end of treatment (during Week 5 for males and Day 12 post partum for females with viable litters, where possible), 5 out of 10 males and 5 out of 10 females were randomly selected from each group for evaluation of sensory reactivity to stimuli of different modalities (e.g. auditory, visual and proprioceptive stimuli) and for assessment of grip strength (ERBC SOP no. ANI/344). Measurements were performed using a computer-generated random order.

- Motor activity assessment (MA):
Once during the study, towards the end of treatment (during Week 5 for males and on Day 12 post partum for females with viable litters where possible), 5 males and 5 females were randomly selected from each group and the motor activity (MA) were measured (for approximately 5 minutes) by an automated activity recording device (ERBC SOP no. ANI/346). Measurements were performed using a computer-generated random order.

- Body weight - Parental animals:
Males were weighed weekly from allocation to termination.
Females were weighed weekly from allocation to positive identification of mating and on Days 0, 7, 14 and 20 post coitum.
Dams were weighed on Days 1, 4, 7, 13 post partum and just before to necropsy.

- Food consumption:
The weight of food consumed by each cage of males and females was recorded weekly (whenever possible) during the pre-mating period starting from Day 1 of dosing up to mating. Individual food consumption for mated females was measured on gestation Days 7, 14 and 20 post coitum starting from Day 0 post coitum and on Day 7 and 13 post partum starting from Day 1 post partum.

- Clinical pathology investigations
Blood collection was performed for hormone determination (0.8 mL) from all parental animals at termination under condition of food deprivation. Blood samples for haematology, clinical chemistry and coagulation were collected by random selection from 5 males and 5 females (females with viable litters) of each group, under condition of food deprivation. Following haematology and coagulation paramaters were assessed: haematocrit, haemoglobin, red blood cell count, reticulocyte count, mean red blood cell volume, mean corpuscular haemoglobin, mean corpuscular haemoglobin concentration, white blood cell count, differential leucocyte count, platelets and prothrobin time. Clinical chemistry parameters assessed corresponds to : alkaline phosphatase, alanine aminotransferase, aspartate aminotransferase, gamma-glutamyltransferase, urea, creatinine, glucose, triglycerides, bile acids, total bilirubin, total cholesterol, total protein, albumin, globulin, A/G Ratio, sodium, potassium, calcium, chloride, inorganic phosphorus.

-Urinalysis (Only males randomly selected)
During the last week of treatment, individual overnight urine samples were also collected from the same animals selected for clinical pathology investigations (5 males/group, randomly selected). Before starting urine collection water bottles were removed from each cage and each animal received approximately 10 mL/kg of drinking water by gavage, in order to obtain urine samples suitable for analysis. The measurements performed on urine samples are as follows: appearance, volume (manually recorded), specific gravity, pH, protein, glucose, ketones, bilirubin, urobilinogen, blood.
These parameters were analysed by Menarini Aution Max AX 4280/Aution Eleven AE 4020, according to in- ternal procedures. The sediment, obtained from centrifugation at approximately 3000 rpm for 10 minutes, was examined microscopically for: epithelial cells, leucocytes, erythrocytes, crystals, spermatozoa and precursors, other abnormal components.

- Blood collection and thyroid hormone determination (T4 and TSH)
Blood collection for hormone determination was performed from all animals at termination.
Males
Blood samples (approximately 0.8 mL) for hormone determination were collected under isoflurane anaesthesia from the retro-orbital sinus. The order of collection was equalised between groups.
Females
As a part of the necropsy procedure, blood samples (approximately 0.8 mL) for hormone determination was withdrawn from the abdominal vena cava under isoflurane anaesthesia. The order of collection was equalised between groups.

- Immunoanalysis - Thyroid hormone determination (T4 and TSH)
Samples were assayed to determine the serum levels of Total thyroxine (total T4) and Thyroid stimulating hormone (TSH) by RadioImmunoAssay (RIA).

Sacrifice and pathology:
-Necropsy
The clinical history of adult animals was studied and a detailed post mortem examination was conducted (including examination of the external surface and orifices). Changes were noted, the requisite organs weighed and the required tissue samples preserved in fixative and processed for histopathological examination.

-Organ weights
From all animals completing the scheduled test period, the organs were dissected free of fat and weighed. The ratios of organ weight to body weight were calculated for each animal.

-Tissues fixed and preserved
Samples of all the tissues (all parental animals) were fixed and preserved in 10% neutral buffered formalin (except eyes, optic nerves and Harderian glands, testes and epididymides which were fixed in modified Davidson’s fluid and preserved in 70% ethyl alcohol).

-Histopathological analyses
After dehydration and embedding in paraffin wax, sections of the tissues were cut at 5 micrometer thickness and stained with haematoxylin and eosin. In addition, the testes and epididymides were cut at 2-3 micrometer thickness and stained with Periodic Acid Schiff (PAS). The morphological evaluation of the seminiferous epithelium (staging of spermatogenic cycle) was performed.

-Sacrifice/Euthanasia: Parental animals and those that had completed the scheduled test period were killed by exsanguinations under isofluorane anaesthesia. The animal sacrificed for humane reasons was killed with carbon dioxide. Pups: Pups killed for humane reasons or those that had completed the scheduled test period (Day 4 post partum or Day 14 post partum) were euthanised by intraperitoneal injection of Sodium Thiopenthal. Pups selected for blood collection for hormone determination were killed on the day of blood sampling. Parental males: The males were killed after the mating of all females (up to Day 35 of the study). Parental females: The females with live pups were killed on Day 14 post partum. One female with total litter loss was killed shortly after the occurrence of total litter loss. The females showing no evidence of copulation were killed 25 days after the last day of the mating session. The females which did not gave birth 25 days after positive identification of mating was killed shortly after
Statistics:
Standard deviations were calculated as appropriate. For variables such as body weight, food consumption, clinical pathology parameters and organ weight, the significance of the differences amongst group means was assessed by Dunnett’s test or a modified t test, depending on the homogeneity of data. Statistical analysis of histopathological findings was carried out by means of the nonparametric Kolmogorov-Smirnov test if n was more than 5. The non-parametric Kruskal-Wallis analysis of variance was used for the other parameters. Intergroup differences between the control and treated groups were assessed by the nonparametric version of the Williams test. The criterion for statistical significance was p<0.05.
Clinical signs:
effects observed, treatment-related
Description (incidence and severity):
Salivation was observed in animals of both sexes dosed at 250 (10 out of 10 males and 5 out of 10 females) and 700 mg/kg/day (all males and females) with a dose-related frequency and incidence, from the first few days of the pre-mating phase up to termination. This treatment-related clinical sign is not considered to be adverse, since no effects on the health status of the affected animals were evident. No clinical signs were observed in animals dosed at 100 mg/kg/day.
Mortality:
no mortality observed
Description (incidence):
No mortality occurred throughout the study.
Body weight and weight changes:
effects observed, non-treatment-related
Description (incidence and severity):
Body weight and body weight gain for male and female animals were generally comparable between the treated and control groups, before and during mating, during gestation and post partum periods.
In a single occasion (Day 0 post coitum), females receiving 700 mg/kg/day showed a very slight but statistically significant decrease in body weight (-5%) compared to the control group. This isolated change was followed by a regular growth of the animals. Due to its occasional occurrence and to its low magnitude, this change was not considered treatment related.
Food consumption and compound intake (if feeding study):
no effects observed
Description (incidence and severity):
Food consumption was unaffected by treatment in both gender during the study.
Food efficiency:
not examined
Water consumption and compound intake (if drinking water study):
not examined
Ophthalmological findings:
not examined
Haematological findings:
effects observed, non-treatment-related
Description (incidence and severity):
No treatment-related changes were recorded.
A statistically significant decrease of monocytes was recorded between control and males dosed at 700mg/kg/day (49%). Values were within the range of historical control data and no other related finding was recorded, therefore this change was considered to be unrelated to treatment.
Clinical biochemistry findings:
no effects observed
Description (incidence and severity):
No effects were obseved.
Endocrine findings:
no effects observed
Description (incidence and severity):
No effects were obseved.
Urinalysis findings:
no effects observed
Description (incidence and severity):
No changes were observed.
Behaviour (functional findings):
no effects observed
Description (incidence and severity):
Observation of animals at removal from the cage and in the open arena (neurotoxicity assessment) did not reveal changes attributable to the test substance, compared to controls.
Immunological findings:
not examined
Organ weight findings including organ / body weight ratios:
no effects observed
Description (incidence and severity):
There were no treatment-related changes in terminal body weight and organ weights when compared to the controls.
Gross pathological findings:
no effects observed
Description (incidence and severity):
There were no treatment-related macroscopic observations at the end of the treatment period. Any macroscopic observations were within the range of occasionally observed and expected spontaneous changes in rats of the same age and therefore considered unrelated to treatment.
Neuropathological findings:
no effects observed
Description (incidence and severity):
No treatment-related alterations in motor activity, grip strength, landing footsplay and sensory reactivity to stimuli were observed in any treatment group at the examination performed at the end of treatment.
Histopathological findings: non-neoplastic:
effects observed, treatment-related
Description (incidence and severity):
Microscopic observations associated with the oral administration of test substance were present in the non glandular region of the stomach of high dose animals of both sexes. Forestomach: treatment-related changes were present in the non-glandular region of the stomach (forestomach) in 4/5 males and 4/5 females of the high dose group and consisted of mild to moderate epithelial hyperplasia (1). Epithelial hyperplasia was associated with hyperkeratosis (thickening of the stratum corneum). Chronic inflammation and oedema were observed in the submucosa in association with the hyperplasia, and, in two instances (animals nos. X1670071 and X1670077), there was also mucosal erosion/ulceration. No treatment-related changes were observed in the non glandular region of the stomach of the selected animals of both sexes from the mid-dose group. Any other microscopic observations other than that listed above had a comparable incidence in control and treated groups and/or are characteristically seen in untreated rats of the same age and were considered incidental and unrelated to treatment. There were no test item-related microscopic observations in the testis (stage aware evaluation on PAS-stained slides).

(1) Toxicologic Pathology, 2016; 29 (1 Suppl): 1S–124S - Thomas Nolte.
Histopathological findings: neoplastic:
not examined
Other effects:
no effects observed
Description (incidence and severity):
Observation of animals at removal from the cage and in the open arena (neurotoxicity assessment) did not reveal changes attributable to the test item, compared to controls.
Key result
Dose descriptor:
NOAEL
Effect level:
700 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
behaviour (functional findings)
body weight and weight gain
clinical biochemistry
food consumption and compound intake
gross pathology
haematology
histopathology: non-neoplastic
mortality
neuropathology
organ weights and organ / body weight ratios
urinalysis
Key result
Critical effects observed:
no
Conclusions:
Under the study conditions, the NOAEL for general toxicity was considered to be 700 mg/kg/day for males and females.
Executive summary:

A combined repeated dose toxicity study with the reproduction / developmental toxicity screening was conducted with the read across substance C16-18 and C18-unsatd. DEA in accordance with OECD 422 and in compliance with GLP. Four groups of ten Sprague Dawley rats (males and females) were exposed by oral gavage to increasing concentrations of the test substance (0, 100, 250 and 700 mg/kg/day). All doses were administered at a constant volume of 10 mL/kg body weight. 0.5% aqueous solution of carboxymethylcellulose was used as a vehicle. According to the study design, males were treated for 14 days prior to pairing and during pairing with females until the day before necropsy, for a total of 33/34 days. Females were treated for 14 days prior to pairing, during pairing and throughout the gestation and lactation periods until Day 13 post-partum, for a total of 43 to 63 days. The following investigations were performed: body weight, clinical signs (including neurotoxicity assessment, motor activity and sensory reactivity to stimuli), food consumption, clinical pathology investigations (haematology and clinical chemistry in five randomly selected animals/sex/group), macroscopic observations, organ weights. Routine histopathological examination was performed in control and high dose groups (five randomly selected animals/sex/group). No mortality occurred throughout the study due to the administration of the test substance. Salivation was the only treatment-related clinical sign recorded in males and females treated at 250 and 700 mg/kg/day, during the study. These clinical signs were not considered to be adverse since no effects on the health status were evident in the affected animals. Neurotoxicity assessment (removal from the home cage and observations in an open arena), motor activity, grip strength and sensory reactivity to stimuli did not reveal changes attributable to the test substance. Body weight and body weight gain of treated animals did not show differences throughout the study when compared to the control group. The food consumption was comparable in all groups. No adverse findings were recorded in clinical pathology investigations (haematology including coagulation parameters and clinical chemistry). Hormone analysis did not show any relation to treatment. Urinalysis in male animals did not reveal changes attributable to the test substance. Changes were observed in the stomach of the majority of males and females dosed at 700mg/kg/day at microscopic examination, due to a local irritant effect of the test substance but these signs were not considered to be severe. Under the study conditions, the NOAEL for general toxicity was considered to be 700 mg/kg/day for males and females (Longobardi, 2022).

Endpoint:
sub-chronic toxicity: oral
Type of information:
experimental study planned (based on read-across)
Study period:
2020-2021
Justification for type of information:
TESTING PROPOSAL ON VERTEBRATE ANIMALS NON-CONFIDENTIAL NAME OF SUBSTANCE:
- Amides, C8-18 (even numbered) and C18-unsatd., N,N-bis(hydroxyethyl (C8-18 and C18-unsatd. DEA), EC No. 931-329-6
CONSIDERATIONS THAT THE GENERAL ADAPTATION POSSIBILITIES OF ANNEX XI OF THE REACH REGULATION ARE NOT ADEQUATE TO GENERATE THE NECESSARY INFORMATION [please address all points below]:
- Available GLP studies : none
- Available non-GLP studies : none
- Historical human data : none
- (Q)SAR : not applicable
- In vitro methods : not applicable
- Weight of evidence : not sufficient
- Grouping and read-across : not sufficient
- Substance-tailored exposure driven testing [if applicable] : none
- Approaches in addition to above [if applicable] : not applicable
- Other reasons [if applicable] : none
CONSIDERATIONS THAT THE SPECIFIC ADAPTATION POSSIBILITIES OF ANNEXES VI TO X (AND COLUMN 2 THEREOF) OF THE REACH REGULATION ARE NOT ADEQUATE TO GENERATE THE NECESSARY INFORMATION:
- Proposed adaptations were not considered sufficient to address this endpoint. This was discussed with ECHA in the frame of a Dossier Improvement Action Plan (DIAP).
FURTHER INFORMATION ON TESTING PROPOSAL IN ADDITION TO INFORMATION PROVIDED IN THE MATERIALS AND METHODS SECTION:
- Proposed study design: according to OECD Guideline 408
Proposed test guideline: according to guideline OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
Principles of method if other than guideline:
Planned study period: As of end 2023 at the earliest depending on testing proposal acceptance.
Qualifier:
according to guideline
Guideline:
OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
GLP compliance:
yes (incl. QA statement)
Species:
rat
Sex:
male/female
Route of administration:
oral: gavage
Remarks on result:
other: Testing planned
Critical effects observed:
not specified
Endpoint:
sub-chronic toxicity: oral
Type of information:
read-across based on grouping of substances (category approach)
Adequacy of study:
supporting study
Study period:
From June 1965 to September 1965
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
study well documented, meets generally accepted scientific principles, acceptable for assessment
Justification for type of information:
Refer to section 13 of IUCLID for details on the category justification.
Reason / purpose for cross-reference:
read-across source
Principles of method if other than guideline:
Rats were administered dietary levels of the test substance at 0, 0.1, 0.5, 1 and 2% for 90 d. The animals were observed daily for clinical signs, body weights were recorded weekly and haematological, clinical chemistry and urine examinations were carried out at termination. Gross and histopathological examinations were also performed.
GLP compliance:
no
Limit test:
no
Species:
rat
Strain:
other: Carworth Farm E
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS

- Age at study initiation: Weanlings
- Housing: Five animals per cage
- Diet: Powdered Spillers Small Laboratory Animal Diet, ad libitum
- Water: Water, ad libitum
Route of administration:
oral: feed
Vehicle:
unchanged (no vehicle)
Analytical verification of doses or concentrations:
no
Duration of treatment / exposure:
90 d
Frequency of treatment:
Daily
Remarks:
0, 0.1, 0.5, 1 and 2% in diet (nominal)
No. of animals per sex per dose:
15
Control animals:
yes, plain diet
Observations and examinations performed and frequency:
CAGE SIDE OBSERVATIONS: Yes

BODY WEIGHT: Yes
- Time schedule for examinations: Day 0 and weekly once thereafter

FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes
- Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg bw/day: Yes
- Time schedule for examinations: Day 0 and weekly once thereafter

HAEMATOLOGY: Yes
- Time schedule for collection of blood: At the end of the study
- Parameters checked in table [No.2]: Total erythrocyte count, hematocrit, hemoglobin, reticulocyte count, total and differential leucocyte counts

CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: At the end of the study
- Parameters examined: Liver and kidney function tests and levels of serum glutamic-oxaloncetic and glutamic-pyruvic transaminases and of blood urea checked

URINALYSIS: Yes
- Time schedule for collection of urine: At the end of the study
- Parameters checked in table [No.3] were examined: Urine was examined for colour, pH, microscopic constituents, protein, reducing substances, bile salts and blood and activity of glutamic-oxaloacetic transaminase. Volume and the specific gravity of the urine excreted were measured during a 6 h period of water deprivation and during 4 h period commencing 16 h after a water load of 25 mL/kg.

OTHER: At autopsy, the absolute and relative organ weight of the brain, heart, liver, kidneys, adrenals and gonads were recorded.
Sacrifice and pathology:
GROSS PATHOLOGY: Yes (At autopsy, the gross appearance of the brain, heart, liver, kidneys, adrenals and gonads were recorded)
HISTOPATHOLOGY: Yes (Paraffin wax sections of brain, heart, liver, kidneys, adrenals and gonads together with a wide range of other organs were stained with haematoxylin and eosin for histological examination, smears of femoral marrow were stained by the May Grunwald-Giemsa method)
Other examinations:
Palatability test: Pairs of male rats were allowed access to stock diet and to diet containing either one of the four dietary test levels of test material. The consumption of both diets was recorded for a period of 8 d.
Clinical signs:
effects observed, treatment-related
Description (incidence and severity):
In general rats remained in good health apart from 2 males on 1% test material which were killed on Days 23 and 58 because of weight loss and respiratory distress.
Mortality:
mortality observed, treatment-related
Description (incidence):
In general rats remained in good health apart from 2 males on 1% test material which were killed on Days 23 and 58 because of weight loss and respiratory distress.
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
Reduced body weight gain was observed from 0.5% onwards.
Food consumption and compound intake (if feeding study):
effects observed, treatment-related
Description (incidence and severity):
Food intake was reduced at all dietary levels except the lowest level of 0.1%.
Food efficiency:
not examined
Water consumption and compound intake (if drinking water study):
not examined
Ophthalmological findings:
not examined
Haematological findings:
effects observed, treatment-related
Description (incidence and severity):
Reductions in hemoglobin levels, hematocrit values and red cell counts in females at 1 and 2% levels but these effects were much less pronounced in males.
Clinical biochemistry findings:
effects observed, treatment-related
Description (incidence and severity):
Serum levels of glutamic-oxaloacetic transaminases were significantly elevated at 0.5% and above in females, but only at 0.5% level in males.
Urinalysis findings:
effects observed, treatment-related
Description (incidence and severity):
Proteinurea was comparable in test and control groups. Tests for blood, bile salts and reducing substances were negative in all groups. Level of Glutamic-oxaloacetic transaminase were significantly elevated at dietary levels of 0.5% and above in females but only at the 0.5% level in males. No significant effect was seen in Glutamic-pyruvic transaminase level at all dietary levels.
Behaviour (functional findings):
not examined
Immunological findings:
not examined
Organ weight findings including organ / body weight ratios:
effects observed, treatment-related
Description (incidence and severity):
The principal organ weight changes were increases in the relative kidney weight in all test groups except at 0.1% in females and at 0.1 and 0.5% in males and increases in relative liver weight in female on the two highest levels.
Gross pathological findings:
no effects observed
Description (incidence and severity):
No significant findings were observed.
Neuropathological findings:
not examined
Histopathological findings: non-neoplastic:
no effects observed
Description (incidence and severity):
Examination of the femoral marrow smears showed no deviation from normality. There were no adverse histopathological findings in any organs.
Histopathological findings: neoplastic:
not examined
Other effects:
not examined
Description (incidence and severity):
OTHER FINDINGS: In the palatability test, exclusive preference was shown to the control diet, virtually no test diet being consumed at any of the dietary levels incorporated. This observation suggests that toxic anorexia was not the cause of reduced food intake.
Key result
Dose descriptor:
NOEL
Effect level:
ca. 0.1 other: %
Based on:
test mat.
Sex:
male/female
Basis for effect level:
other: see 'Remark'
Key result
Critical effects observed:
yes
Lowest effective dose / conc.:
0.5 other: %
Organ:
other: bodyweight
Treatment related:
no

For detailed results tables kindly refer to the attached background materials section of the IUCLID.

Conclusions:
Under the study conditions, the 90 d NOEL in rats was considered to be 0.1% in the diet, equivalent to 50 mg/kg bw/day.
Executive summary:

A study was conducted to evaluate the repeated dose oral toxicity of the read across substance, C12 DEA. The rats were administered read across substance concentrations of 0, 0.1, 0.5, 1 and 2% in diet for 90 d. The animals were observed daily for clinical signs. Body weight were recorded weekly and haematological, clinical chemistry and urine examinations were carried out at termination. Gross and histopathological examinations were also performed at termination. No adverse effect on the appearance or condition of the animals was observed. Growth retardation was associated with diminished food intake from the dose level of 0.5%. Food refusal was demonstrably due to an effect of the test material on palatability of the diet. Terminal haematological examination revealed a reduction in the haemoglobin level, haematocrit and red cell count at the 1 and 2% dose levels in females but less pronounced effects were seen in males. Serum levels of glutamic-oxaloacetic transaminase were elevated at 0.5% and above in females but only at 0.5 % in males. No untoward effect was observed in the renal function tests. The principal organ weight changes were: increases in the relative kidney weight in all test groups except at 0.1% in females and at 0.1 and 0.5% in males, and increases in the relative liver weight in females on the two highest levels. The types and incidence of histological lesions were comparable in control and test groups. Under the study conditions, the 90 d NOEL in rats was considered to be 0.1% in the diet, equivalent to 50 mg/kg bw/day (Gaunt, 1965).


However, as it was unclear whether the effects noted were related to the test substance itself or were the result of nutritional deficiencies due to the unpalatability of the diet, this study was not taken into account for DNEL derivation.

Endpoint conclusion
Endpoint conclusion:
no adverse effect observed
Dose descriptor:
NOAEL
700 mg/kg bw/day
Study duration:
subacute
Species:
rat

Repeated dose toxicity: inhalation - systemic effects

Link to relevant study records
Reference
Endpoint:
short-term repeated dose toxicity: inhalation
Data waiving:
study scientifically not necessary / other information available
Justification for data waiving:
other:
Critical effects observed:
not specified
Endpoint conclusion
Endpoint conclusion:
no study available

Repeated dose toxicity: inhalation - local effects

Endpoint conclusion
Endpoint conclusion:
no study available

Repeated dose toxicity: dermal - systemic effects

Link to relevant study records

Referenceopen allclose all

Endpoint:
sub-chronic toxicity: dermal
Type of information:
read-across based on grouping of substances (category approach)
Adequacy of study:
supporting study
Study period:
Not available
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
test procedure in accordance with generally accepted scientific standards and described in sufficient detail
Remarks:
KL2 due to RA
Justification for type of information:
Refer to the section 13 for details on the category justification.
Reason / purpose for cross-reference:
read-across source
Reason / purpose for cross-reference:
reference to other study
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 411 (Subchronic Dermal Toxicity: 90-Day Study)
Deviations:
not specified
Principles of method if other than guideline:
The test substance was applied daily to the skin in graduated doses to several groups of mice, one dose per group, for a period of 14 wk. During the period of application the animals are observed daily to detect signs of toxicity. Animals which die during the test are necropsied, and at the conclusion of the test the surviving animals were sacrificed and necropsied.
GLP compliance:
yes
Limit test:
no
Species:
mouse
Strain:
B6C3F1
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Taconic Farms, Germantown, NY
- Age at study initiation: 6 wk
- Housing: Housed individually in Polycarbonate cages (Lab Products, Inc., Maywood, NJ)
- Bedding: Sani-Chip heat-treated hardwood chips (PJ Murphy Forest Products Corp., Montville, NJ)
- Diet : NIH-07 open formula pelleted diet (Zeigler Brothers, Inc., Gardners, PA), ad libitum
- Water : Tap water (Columbus municipal supply), ad libitum
- Acclimation period: 16 to 17 d

ENVIRONMENTAL CONDITIONS
- Temperature : 20.6-22.8°C
- Humidity : 41-58%
- Air changes : 10/hr
- Photoperiod : 12 h dark/12 h light

IN-LIFE DATES: From: Feb. 12, 1992 To: May 15, 1992

Type of coverage:
open
Vehicle:
ethanol
Details on exposure:
The test material formulations were applied on shaved skin of the test animals.


Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
Periodic analyses of the dose formulations of test material were conducted at the study laboratory using HPLC. Dose formulations from the beginning, middle, and end of the studies were analyzed
Duration of treatment / exposure:
14 wk
Frequency of treatment:
5 exposures/wk
Dose / conc.:
0 mg/kg bw/day (nominal)
Dose / conc.:
50 mg/kg bw/day (nominal)
Remarks:
Corresponding to 20 mg/mL in ethanol
Dose / conc.:
100 mg/kg bw/day (nominal)
Remarks:
Corresponding to 40 mg/mL in ethanol
Dose / conc.:
200 mg/kg bw/day (nominal)
Remarks:
Corresponding to 80 mg/mL in ethanol
Dose / conc.:
400 mg/kg bw/day (nominal)
Remarks:
Corresponding to 160 mg/mL in ethanol
Dose / conc.:
800 mg/kg bw/day (nominal)
Remarks:
Corresponding to 320 mg/mL in ethanol
No. of animals per sex per dose:
10/sex/dose group
Control animals:
yes, concurrent vehicle
Details on study design:
No information




Positive control:
Not applicable
Observations and examinations performed and frequency:
CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Twice daily

DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Weekly once

BODY WEIGHT: Yes
- Time schedule for examinations: Weighed initially, weekly, and at the end of the studies

OTHER: Organs weighed were heart, right kidney, liver, lung, right testis, and thymus
Sacrifice and pathology:
SACRIFICE: Yes (Carbon dioxide asphyxiation)

GROSS PATHOLOGY: Yes

HISTOPATHOLOGY: Yes. Complete histopathology was performed on 0 and 800 mg/kg bw mice. In addition to gross lesions and tissue masses, the following tissues were examined: adrenal gland, bone and marrow, brain, clitoral gland, esophagus, gallbladder, heart, large intestine (cecum, colon, rectum), small intestine (duodenum, jejunum, ileum), kidney, liver, lung, lymph nodes (mandibular and mesenteric), mammary gland, nose, ovary, pancreas, parathyroid gland, pituitary gland, preputial gland, prostate gland, salivary gland, spleen, stomach (forestomach and glandular), testis (and epididymis and seminal vesicle), thymus, thyroid gland, trachea, urinary bladder, and uterus.
Other examinations:
Sperm motility and vaginal cytology: At the end of the studies, samples were collected for sperm motility or vaginal cytology from mice of 200, 400 and 800 mg/kg bw groups. The following sperm motility parameters were evaluated: spermatid heads per gram of testis, spermatid heads per testis, spermatid count, and epididymal spermatozoal motility and concentration. The left cauda epididymis, epididymis, and testis were weighed. Vaginal samples for cytology evaluations were collected for 12 consecutive days prior to the end of the studies from all female mice. The length of the estrous cycle and the length of time spent in each stage of the cycle were evaluated.
Statistics:
Survival Analyses: The probability of survival was estimated by the product-limit procedure of Kaplan and Meier (1958). Possible dose-related effects on survival were analysed by Cox’s (1972) method for testing two groups for equality and Tarone’s (1975) life table test to identify dose-related trends. All reported P values for the survival analyses were two-sided.

Analysis of Neoplasm and Nonneoplastic Lesion Incidences: The Poly-k test (Bailer and Portier, 1988; Portier and Bailer, 1989; Piegorsch and Bailer, 1997) was used to assess neoplasm and nonneoplastic lesion prevalence. Tests of significance included pairwise comparisons of each dosed group with controls and a test for an overall dose-related trend. Continuity-corrected tests were used in the analysis of lesion incidence, and reported P values are one sided.

Analysis of Continuous Variables: Organ and body weight data, which historically have approximately normal distributions, were analyzed with the parametric multiple comparison procedures of Dunnett (1955) and Williams (1971, 1972). Jonckheere's test (Jonckheere, 1954) was used to assess the significance of the dose-related trends. Average severity values were analyzed for significance with the Mann-Whitney U test. Treatment effects were investigated by applying a multivariate analysis of variance (Morrison, 1976) to the transformed data to test for simultaneous equality of measurements across dose levels.
Clinical signs:
effects observed, treatment-related
Description (incidence and severity):
The only treatment related clinical finding was irritation of the skin at the site of application in males and females administered 800 mg/kg bw.
Dermal irritation:
effects observed, treatment-related
Description (incidence and severity):
The only treatment related clinical finding was irritation of the skin at the site of application in males and females administered 800 mg/kg bw.
Mortality:
mortality observed, treatment-related
Description (incidence):
All mice survived until the end of the study.
Body weight and weight changes:
no effects observed
Description (incidence and severity):
Final mean body weights and body weight gains of dosed males and females were similar to those of the vehicle controls.
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:
not examined
Urinalysis findings:
not examined
Behaviour (functional findings):
not examined
Organ weight findings including organ / body weight ratios:
effects observed, treatment-related
Description (incidence and severity):
The absolute and relative liver and right kidney weights of 800 mg/kg bw males and females and the absolute and relative liver weights of 400 mg/kg bw females were significantly greater than those of the vehicle controls. The absolute and relative lung weights of 800 mg/kg bw females were also significantly greater than those of the vehicle controls.
Gross pathological findings:
no effects observed
Histopathological findings: non-neoplastic:
effects observed, treatment-related
Description (incidence and severity):
Histopathologic lesions of the skin at the site of application included epidermal hyperplasia, sebaceous gland hyperplasia, chronic active inflammation, parakeratosis, and ulcer. The incidences and severities of these skin lesions generally increased with increasing dose in males and females.
Histopathological findings: neoplastic:
not examined
Other effects:
effects observed, treatment-related
Description (incidence and severity):
Epididymal spermatozoal concentration was significantly increased in 800 mg/kg bw males. Estrous cycle lengths of dosed females were similar to that of the vehicle controls.

Key result
Dose descriptor:
NOAEL
Effect level:
ca. 50 mg/kg bw/day (nominal)
Sex:
male/female
Basis for effect level:
other: Overall effects
Critical effects observed:
not specified

For detailed tables kindly refer to the attached background materials section of the IUCLID.

Conclusions:
Under the study conditions, the 14-week NOAEL in mice for systemic effects was considered to be 200 mg/kg bw/day and for the local effects 100 mg/kg bw/day.
Executive summary:

A study was conducted to evaluate the repeated dose dermal toxicity of the read across substance, C8-18 and C18-unsatd. DEA, according to design based on OECD Guideline 411, in compliance with GLP. Groups of 10 male and 10 female mice were exposed to 0, 50, 100, 200, 400 or 800 mg/kg bw/day of the substance in ethanol by dermal application, 5 times per week, for 14 weeks. Mortality, clinical signs and bodyweight were recorded throughout the study. At the end of the study, samples were collected for sperm motility and vaginal cytology evaluations in the 0, 200, 400 and 800 mg/kg bw/day dose groups. At necropsy, a gross macroscopic examination was conducted. Selected organs were weighed and a complete histopathological evaluation was carried out for 0 and 800 mg/kg bw/day mice. All mice survived until the end of the study. The only treatment related clinical finding was irritation of the skin at the site of application in males and females administered 800 mg/kg bw/day. There were no effects on body weight. Weights of the liver and kidney of 800 mg/kg bw/day males and females, liver of 400 mg/kg bw/day females and lung of 800 mg/kg bw/day females were significantly increased compared to the controls. Epididymal spermatozoa concentration was significantly increased in 800 mg/kg bw/day males. Histopathologic lesions of the skin at the site of application included epidermal hyperplasia, sebaceous gland hyperplasia, chronic active inflammation, parakeratosis and ulcer. The incidences and severities of these skin lesions generally increased with increasing dose in males and females. Under the study conditions, the 14-week NOAEL in mice for systemic effects was considered to be 200 mg/kg bw/day and for the local effects 100 mg/kg bw/day (Irwin, 2001).

Endpoint:
sub-chronic toxicity: dermal
Type of information:
read-across based on grouping of substances (category approach)
Adequacy of study:
supporting study
Study period:
Not available
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
test procedure in accordance with generally accepted scientific standards and described in sufficient detail
Remarks:
KL2 due to RA
Justification for type of information:
Refer to the section 13 for details on the category justification.
Reason / purpose for cross-reference:
read-across source
Reason / purpose for cross-reference:
reference to other study
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 411 (Subchronic Dermal Toxicity: 90-Day Study)
Deviations:
not specified
Principles of method if other than guideline:
The test substance is applied daily to the skin in graduated doses to several groups of experimental animals, one dose per group, for a period of 14 wk. During the period of application the animals are observed daily to detect signs of toxicity. Animals which die during the test are necropsied, and at the conclusion of the test the surviving animals were sacrificed and necropsied.
GLP compliance:
yes
Limit test:
no
Species:
rat
Strain:
Fischer 344
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Taconic Farms, Germantown, NY
- Age at study initiation: 6 wk
- Housing: Housed individually in Polycarbonate cages (Lab Products, Inc., Maywood, NJ)
- Bedding: Sani-Chip heat-treated hardwood chips (PJ Murphy Forest Products Corp., Montville, NJ)
- Diet : NIH-07 open formula pelleted diet (Zeigler Brothers, Inc., Gardners, PA), ad libitum
- Water : Tap water (Columbus municipal supply), ad libitum
- Acclimation period: 14 to 15 d

ENVIRONMENTAL CONDITIONS
- Temperature : 22.2-23.9°C
- Humidity : 38-55%
- Air changes : 10/hr
- Photoperiod : 12 h dark/12 h light

IN-LIFE DATES: From: Feb. 10, 1992 To: May 13, 1992

Type of coverage:
open
Vehicle:
ethanol
Details on exposure:
Not reported


Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
Periodic analyses of the dose formulations of test material were conducted at the study laboratory using HPLC. Dose formulations from the beginning, middle, and end of the studies were analysed.
Duration of treatment / exposure:
14 wk
Frequency of treatment:
5 exposures/wk
Dose / conc.:
0 mg/kg bw/day (nominal)
Dose / conc.:
25 mg/kg bw/day (nominal)
Remarks:
Corresponding to 30 mg/mL in ethanol
Dose / conc.:
50 mg/kg bw/day (nominal)
Remarks:
Corresponding to 61 mg/mL in ethanol
Dose / conc.:
100 mg/kg bw/day (nominal)
Remarks:
Corresponding to 121 mg/mL in ethanol
Dose / conc.:
200 mg/kg bw/day (nominal)
Remarks:
Corresponding to 243 mg/mL in ethanol
Dose / conc.:
400 mg/kg bw/day (nominal)
Remarks:
Corresponding to 485 mg/mL in ethanol
No. of animals per sex per dose:
10/sex/dose in the core study, 10/sex/dose for clinical pathology groups
Control animals:
yes, concurrent vehicle
Details on study design:
No information




Positive control:
Not applicable
Observations and examinations performed and frequency:
CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Twice daily

DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Weekly once

BODY WEIGHT: Yes
- Time schedule for examinations: Weighed initially, weekly, and at the end of the studies

HAEMATOLOGY: Yes
- Time schedule for collection of blood: On days 4 and 24 (blood was collected from the retroorbital sinus of clinical pathology study male and female rats from each dose group)
- Anaesthetic used for blood collection: Yes (carbon dioxide/oxygen mixture)
- How many animals: All animals
- Parameters examined.: Hematocrit; hemoglobin concentration; erythrocyte, reticulocyte, nucleated erythrocyte, and platelet counts; mean cell volume; mean cell hemoglobin; mean cell hemoglobin concentration; and leukocyte count and differentials

CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: On days 4 and 24 (blood was collected from the retroorbital sinus of clinical pathology study male and female rats from each dose group)
- How many animals: All animals
- Parameters examined: Urea nitrogen, creatinine, total protein, albumin, cholesterol, triglycerides, alanine aminotransferase, alkaline phosphatase, sorbitol dehydrogenase, and total bile acids

OTHER: Organs weighed were heart, right kidney, liver, lung, right testis, and thymus
Sacrifice and pathology:
SACRIFICE: At the end of the 14 wk studies, blood was collected from the retroorbital sinus of all core study rats for hematology and clinical chemistry analyses. Thereafter the test animals were anesthetised with a carbon dioxide/oxygen mixture.

GROSS PATHOLOGY: Yes

HISTOPATHOLOGY: Yes. Complete histopathology was performed on 0 and 400 mg/kg bw. In addition to gross lesions and tissue masses, the following tissues were examined: heart, large intestine (cecum, colon, rectum), small intestine (duodenum, jejunum, ileum), kidney, liver, lung, lymph nodes (mandibular and mesenteric), mammary gland, nose, ovary, pancreas, parathyroid gland, pituitary gland, preputial gland, prostate gland, salivary gland, spleen, stomach (forestomach and glandular), testis (and epididymis and seminal vesicle), thymus, thyroid gland, trachea, urinary bladder, and uterus. In addition, the skin (site of application) was examined in all core study animals, and the kidney was examined in core study male and female rats.
Other examinations:
Sperm motility and vaginal cytology: At the end of the studies, samples were collected for sperm motility or vaginal cytology from all rats receiving 100, 200 and 400 mg/kg bw of test material. The following sperm motility parameters were evaluated: spermatid heads per gram of testis, spermatid heads per testis, spermatid count, and epididymal spermatozoal motility and concentration. The left cauda epididymis, epididymis, and testis were weighed. Vaginal samples for cytology evaluations were collected for 12 consecutive days prior to the end of the studies from all female rats. The length of the estrous cycle and the length of time spent in each stage of the cycle were evaluated.
Statistics:
Survival Analyses: The probability of survival was estimated by the product-limit procedure of Kaplan and Meier (1958). Possible dose-related effects on survival were analysed by Cox’s (1972) method for testing two groups for equality and Tarone’s (1975) life table test to identify dose-related trends. All reported P values for the survival analyses were two-sided.

Analysis of Neoplasm and Nonneoplastic Lesion Incidences: The Poly-k test (Bailer and Portier, 1988; Portier and Bailer, 1989; Piegorsch and Bailer, 1997) was used to assess neoplasm and nonneoplastic lesion prevalence. Tests of significance included pairwise comparisons of each dosed group with controls and a test for an overall dose-related trend. Continuity-corrected tests were used in the analysis of lesion incidence, and reported P values are one sided.

Analysis of Continuous Variables: Organ and body weight data, which historically have approximately normal distributions, were analyzed with the parametric multiple comparison procedures of Dunnett (1955) and Williams (1971, 1972). Jonckheere's test (Jonckheere, 1954) was used to assess the significance of the dose-related trends. Average severity values were analyzed for significance with the Mann-Whitney U test. Treatment effects were investigated by applying a multivariate analysis of variance (Morrison, 1976) to the transformed data to test for simultaneous equality of measurements across dose levels.
Clinical signs:
effects observed, treatment-related
Description (incidence and severity):
Clinical findings included irritation of the skin at the site of application in 100, 200, and 400 mg/kg bw males and females.
Dermal irritation:
effects observed, treatment-related
Description (incidence and severity):
Clinical findings included irritation of the skin at the site of application in 100, 200, and 400 mg/kg bw males and females.
Mortality:
mortality observed, treatment-related
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
Final mean body weights and body weight gains of 200 and 400 mg/kg bw males and females were significantly less than those of the vehicle controls.
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:
effects observed, treatment-related
Description (incidence and severity):
At week 14, a minimal microcytic, normochromic, nonresponsive anemia occurred in the 100 and 200 mg/kg bw females and 400 mg/kg bw males and females. The anemia also occurred in the 400 mg/kg bw males and females on day 24. Increased segmented neutrophil counts occurred in 400 mg/kg bw males and females at week 14 and in 400 mg/kg bw females on day 24.
Clinical biochemistry findings:
effects observed, treatment-related
Description (incidence and severity):
Cholesterol concentrations were significantly decreased in 200 and 400 mg/kg bw males and in females administered 100 mg/kg bw or greater; triglyceride concentrations were also decreased in 200 and 400 mg/kg bw males. At week 14, there was a minimal concentration-related increase of serum albumin concentration in all treated groups of females and in 100 mg/kg bw or greater male rats; on day 24, increased albumin concentration occurred in the 400 mg/kg bw females. There were minimal increases of urea nitrogen concentration that occurred in the 200 and 400 mg/kg bw female rats on day 24 and at week 14. At week 14, an increase in alanine aminotransferase activity occurred in 50 mg/kg bw or greater male rats. Additionally, alkaline phosphatase activity was increased in 400 mg/kg bw males.
Urinalysis findings:
not examined
Behaviour (functional findings):
not examined
Organ weight findings including organ / body weight ratios:
effects observed, treatment-related
Description (incidence and severity):
Kidney weights of females administered 50 mg/kg bw or greater were significantly greater than those of the vehicle control group. Left epididymis weights of 200 and 400 mg/kg bw males were significantly less than those of the vehicle controls, but this was most likely secondary to decreased mean body weights in these groups.
Gross pathological findings:
no effects observed
Histopathological findings: non-neoplastic:
effects observed, treatment-related
Description (incidence and severity):
Histopathologic lesions of the skin at the site of application included epidermal hyperplasia, sebaceous gland hyperplasia, chronic active inflammation, parakeratosis, and ulcer. The incidences and severities of these skin lesions generally increased with increasing dose in males and females. The incidences of renal tubule regeneration in 100, 200, and 400 mg/kg bw females were significantly greater than the vehicle control incidence, and the severities in 200 and 400 mg/kg bw females were increased.
Histopathological findings: neoplastic:
not examined
Other effects:
no effects observed
Description (incidence and severity):
Estrous cycle lengths of dosed females were similar to those of the vehicle controls.
Key result
Dose descriptor:
NOAEL
Effect level:
ca. 50 mg/kg bw/day (nominal)
Sex:
male/female
Basis for effect level:
other: Overall effects
Critical effects observed:
not specified

For detailed tables kindly refer to the attached background materials section of the IUCLID.

Conclusions:
Under the study conditions, the 14-week systemic NOAEL in rats was considered to be 50 mg/kg bw/day.
Executive summary:

A study was conducted to evaluate the repeated dose toxicity of the read across substance, C8-18 and C18-unsatd. DEA, according to design based on OECD Guideline 411, in compliance with GLP. Groups of 10 male and 10 female rats were exposed to 0, 25, 50, 100, 200 or 400 mg/kg bw/day of the substance in ethanol by dermal application, 5 times per week, for 14 weeks. Mortality, clinical signs and bodyweight were recorded throughout the study. Blood was collected on days 4 and 24 for hematology and clinical chemistry analysis. At the end of the study, samples were collected for sperm motility and vaginal cytology evaluations in the 0, 100, 200 or 400 mg/kg bw/day dose groups. At necropsy, a gross macroscopic examination was conducted. Selected organs were weighed and a complete histopathological evaluation was carried out for 0 and 400 mg/kg/day rats. All rats survived until the end of the study. Clinical findings included irritation of the skin at the site of application in 100, 200 and 400 mg/kg bw/day males and females. Final mean bodyweights and bodyweight gains of 200 and 400 mg/kg bw/day males and females were significantly lower than those of the controls. At week 14, a minimal microcytic, normochromic, non-responsive anaemia occurred in the 100 and 200 mg/kg bw/day females and 400 mg/kg bw/day males and females. The anaemia was also seen in the 400 mg/kg bw/day males and females on day 24. Increased segmented neutrophil counts occurred in 400 mg/kg bw/day males and females at week 14 and in 400 mg/kg bw/day females on day 24. Cholesterol concentrations were significantly decreased in 200 and 400 mg/kg bw/day males and in females administered 100 mg/kg bw/day or greater. Triglyceride concentrations were decreased in 200 and 400 mg/kg bw/day males. Histopathological lesions of the skin at the site of application included epidermal hyperplasia, sebaceous gland hyperplasia, chronic active inflammation, parakeratosis and ulcer. The incidence and severity of these skin lesions generally increased with increasing dose in males and females. The incidences of renal tubule regeneration in 100, 200 and 400 mg/kg bw/day females were significantly greater than in controls, and the severity in 200 and 400 mg/kg bw/day females was increased. Under the study conditions, the 14-week systemic NOAEL in rats was considered to be 50 mg/kg bw/day (Irwin, 2001).

Endpoint:
chronic toxicity: dermal
Type of information:
read-across based on grouping of substances (category approach)
Adequacy of study:
supporting study
Study period:
Not available
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
test procedure in accordance with generally accepted scientific standards and described in sufficient detail
Remarks:
KL2 due to RA
Justification for type of information:
Refer to the section 13 for details on the category justification.
Reason / purpose for cross-reference:
read-across source
Reason / purpose for cross-reference:
reference to other study
Principles of method if other than guideline:
A two-year dermal study was conducted in mice to evaluate the carcinogenic potential of the test substance.
GLP compliance:
yes
Limit test:
no
Species:
mouse
Strain:
B6C3F1
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Taconic Laboratory Animals and Services, (Germantown, NY)
- Age at study initiation: 6 wk
- Housing: Housed individually in Polycarbonate cages (Lab Products, Inc., Maywood, NJ)
- Bedding: Sani-Chip heat-treated hardwood chips (PJ Murphy Forest Products Corp., Montville, NJ)
- Diet : NIH-07 open formula pelleted diet (Zeigler Brothers, Inc., Gardners, PA), ad libitum
- Water : Tap water (Columbus municipal supply), ad libitum
- Acclimation period: 13 to 14 d

ENVIRONMENTAL CONDITIONS
- Temperature : 20.6-23.9°C
- Humidity : 30-67%
- Air changes : 10/hr
- Photoperiod : 12 h dark/12 h light

IN-LIFE DATES: From: Jan. 20, 1993 To: Jan. 20, 1995
Type of coverage:
open
Vehicle:
ethanol
Details on exposure:
The test material formulation was applied to the shaved skin of test animals. No further details provided.
Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
Dose formulations were analysed approximately every 2 months using HPLC. In addition to dose formulation analysis prior to dosing, samples collected after dosing (animal room samples) were analysed periodically. All dose formulations analysed during the 2 year studies were within 10% of the target concentration.

Duration of treatment / exposure:
104 wk
Frequency of treatment:
Five exposures per week

Dose / conc.:
0 mg/kg bw/day (nominal)
Dose / conc.:
100 mg/kg bw/day (nominal)
Remarks:
Corresponding to 50 mg/mL in ethanol
Dose / conc.:
200 mg/kg bw/day (nominal)
Remarks:
Corresponding to 100 mg/mL in ethanol
No. of animals per sex per dose:
50/sex/dose
Control animals:
yes, concurrent vehicle
Details on study design:
Dose selection rationale: Exposure to coconut oil acid diethanolamine condensate in the 14-wk study produced only a minimal toxic response in mice except in the skin at the site of application. The incidences of chronic active inflammation as well as several other skin lesions were significantly increased at doses of 200 mg/kg bw and greater in both male and female mice. The incidences of ulceration were increased in males exposed to 400 and 800 mg/kg bw and in females exposed to 800 mg/kg bw. Therefore, 400 and 800 mg/kg bw were considered inappropriate for a 2-year study. However, ulceration was present in only one 200 mg/kg bw male and no females, and the severities of these lesions in all affected groups were minimal to mild. Below 200 mg/kg bw, the incidences of skin lesions decreased markedly with a minor difference in response between 50 and 100 mg/kg bw. Therefore, 200 mg/kg bw was selected as the high dose and 100 mg/kg bw as the low dose for this 2-yr study.
Observations and examinations performed and frequency:
CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Observed twice daily

DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Clinical findings were recorded initially, at 4 wk intervals during the study, and at the end of the study

DERMAL IRRITATION (if dermal study): Yes

BODY WEIGHT: Yes
- Time schedule for examinations: Animals were weighed initially, weekly during week 1 through 13, at 4 wk intervals thereafter, and at the end of the studies


Sacrifice and pathology:
SACRIFICE: Carbon dioxide asphyxiation

GROSS PATHOLOGY: Yes

HISTOPATHOLOGY: Yes, Complete histopathology was performed on all rats. In addition to gross lesions and tissue masses, the following tissues were examined: adrenal gland, bone and marrow, brain, clitoral gland, esophagus, heart, large intestine (cecum, colon, rectum), small intestine (duodenum, jejunum, ileum), kidney, liver, lung, lymph nodes (mandibular and mesenteric), mammary gland, nose, ovary, pancreas, parathyroid gland, pituitary gland, preputial gland, prostate gland, salivary gland, skin, spleen, stomach (forestomach and glandular), testis (and epididymis and seminal vesicle), thymus, thyroid gland, trachea, urinary bladder, and uterus.
Statistics:
Survival Analyses: The probability of survival was estimated by the product-limit procedure of Kaplan and Meier (1958). Possible dose-related effects on survival were analysed by Cox’s (1972) method for testing two groups for equality and Tarone’s (1975) life table test to identify dose-related trends. All reported P values for the survival analyses were two-sided.

Analysis of Neoplasm and Nonneoplastic Lesion Incidences: The Poly-k test (Bailer and Portier, 1988; Portier and Bailer, 1989; Piegorsch and Bailer, 1997) was used to assess neoplasm and nonneoplastic lesion prevalence. Tests of significance included pairwise comparisons of each dosed group with controls and a test for an overall dose-related trend. Continuity-corrected tests were used in the analysis of lesion incidence, and reported P values are one sided.

Analysis of Continuous Variables: Organ and body weight data, which historically have approximately normal distributions, were analyzed with the parametric multiple comparison procedures of Dunnett (1955) and Williams (1971, 1972). Jonckheere's test (Jonckheere, 1954) was used to assess the significance of the dose-related trends. Average severity values were analyzed for significance with the Mann-Whitney U test. Treatment effects were investigated by applying a multivariate analysis of variance (Morrison, 1976) to the transformed data to test for simultaneous equality of measurements across dose levels.
Clinical signs:
effects observed, treatment-related
Description (incidence and severity):
The only treatment-related clinical finding was irritation of the skin at the site of application in males that received 200 mg/kg bw.
Dermal irritation:
effects observed, treatment-related
Description (incidence and severity):
The only treatment-related clinical finding was irritation of the skin at the site of application in males that received 200 mg/kg bw.
Mortality:
mortality observed, treatment-related
Description (incidence):
The survival of dosed males and 100 mg/kg bw females was similar to that of the vehicle controls. Survival of the 200 mg/kg bw group of female mice was reduced compared to the vehicle control group, but the difference was not significant.
Body weight and weight changes:
effects observed, treatment-related
Description (incidence and severity):
Mean body weights of dosed males were similar to those of the vehicle controls throughout most of the study; those of 100 and 200 mg/kg bw females were less than those of the vehicle controls from wk 93 and 77, respectively .
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:
not examined
Urinalysis findings:
not examined
Behaviour (functional findings):
not examined
Organ weight findings including organ / body weight ratios:
no effects observed
Gross pathological findings:
effects observed, treatment-related
Histopathological findings: non-neoplastic:
effects observed, treatment-related
Description (incidence and severity):
Skin: Several nonneoplastic lesions of the skin at the site of application were determined to be chemical related. Incidences of epidermal hyperplasia, sebaceous gland hyperplasia, and hyperkeratosis in all dosed groups of males and females were significantly greater than those in the vehicle control groups. The incidences of ulceration in 200 mg/kg bw males and inflammation and parakeratosis in 200 mg/kg bw females were increased.
Histopathological findings: neoplastic:
effects observed, treatment-related
Description (incidence and severity):
Liver: Dosed male and female mice had significantly greater incidences of hepatic neoplasms (hepatocellular adenoma, hepatocellular carcinoma, and hepatoblastoma (males) than the vehicle controls. There was a morphologic continuum from adenoma to carcinoma, with less differentiation and typical trabecular formations in the carcinomas. Carcinomas were often a centimeter or more in diameter, whereas adenomas were generally smaller and more discrete. Carcinomas metastasized to the lung in a few males and females. Adenomas, carcinomas, and hepatoblastomas displaced normal liver parenchyma, and none contained normal lobular architecture. Hepatoblastomas were characterized by well-demarcated focal areas composed of bundles of deeply basophilic, spindle-shaped cells.

Kidney: The incidences of renal tubule adenoma (1/50, 1/50, 7/50) and of renal tubule adenoma or carcinoma (combined) (1/50, 1/50, 9/50) in 200 mg/kg bw males were significantly greater than those in the vehicle controls. Renal tubule hyperplasia, adenoma, and carcinoma formed a morphological continuum. Adenomas were focal, compressive masses approximately five or more tubules in diameter; carcinomas were morphologically similar to adenomas but were larger and often showed cellular debris and/or mineralization. Renal tubule neoplasms were located in the cortex or outer medulla. Focal proliferative masses less than five tubules in diameter were classified as focal hyperplasia.

Thyroid Gland: The incidences of follicular cell hyperplasia in all dosed groups of males (vehicle control, 11/50; 100 mg/kg bw, 20/50; 200 mg/kg bw, 23/50) and females (27/50, 36/50, 33/50) were significantly greater than those in the vehicle controls. Follicular cell hyperplasia consisted of focal areas of thyroid gland follicles lined with increased numbers of epithelial cells, which formed papillary projections in some instances.
Key result
Dose descriptor:
LOAEL
Remarks:
(systemic and local effects)
Effect level:
ca. 100 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
other: based on body weight changes, thyroid gland follicular cell hyperplasia, hepatic neoplasms, renal tubule adenoma, and several non-neoplastic lesions of the skin at all dose levels.
Critical effects observed:
not specified

For detailed tables kindly refer to the attached background materials section of the IUCLID.

 

Conclusions:
Under the study conditions, the 2-yr LOAEL was considered to be 100 mg/kg bw/day in mouse.
Executive summary:

A study was conducted to evaluate the long-term repeated dose dermal toxicity of the read across substance, C8-18 and C18-unsatd. DEA, in compliance with GLP. The doses studied included 0, 100 and 200 mg/kg bw/day of read across substance (corresponding to 0, 50, or 100 mg/mL in ethanol). Fifty male/female test animals were used in each group. Five exposures per week were administered for 104 to 105 weeks. The animals were observed twice daily, and body weights and clinical findings were recorded periodically. All animals were necropsied and complete histopathology was performed. Survival of dosed male and female mice was generally similar to that of the vehicle controls. The mean bodyweights of the 100 mg/kg bw/day females from week 93 and of the 200 mg/kg bw/day females from week 77 were lower than those of the vehicle controls. The only clinical finding attributed to treatment was an irritation of the skin at the site of application in males administered 200 mg/kg bw/day. The incidences of hepatic neoplasms (hepatocellular adenoma, hepatocellular carcinoma and hepatoblastoma) were significantly increased in male and/or female mice. The number of eosinophilic foci in dosed groups of male mice was higher than in the vehicle controls. The occurrences of renal tubule adenoma and renal tubule adenoma or carcinoma (combined) were significantly increased in 200 mg/kg bw/day males. Several non-neoplastic lesions of the skin at the site of application were considered treatment-related. Incidences of epidermal hyperplasia, sebaceous gland hyperplasia and hyperkeratosis were greater in all dosed groups than in the vehicle controls and the number of thyroid gland follicular cell hyperplasia in all dosed groups was also significantly greater than those in the vehicle control groups. There was clear evidence of carcinogenic activity in male B6C3F1 mice based on increased incidences of hepatic and renal tubule neoplasms and in female B6C3F1 mice based on increased incidences of hepatic neoplasms. These increases were associated with the concentration of free diethanolamine present as a contaminant in the read across substance. However, recent evidence suggests that DEA should not be classified as a carcinogen, as the hepatic tumours seen in mice and the proposed mode of non-genotoxic mechanism for renal/liver tumours are not relevant to humans/primates. Under the study conditions, the 2-yr LOAEL was considered to be 100 mg/kg bw/day in mouse (Irwin, 2001).

Endpoint:
chronic toxicity: dermal
Type of information:
read-across based on grouping of substances (category approach)
Adequacy of study:
key study
Study period:
Not available
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
test procedure in accordance with generally accepted scientific standards and described in sufficient detail
Remarks:
KL2 due to RA
Justification for type of information:
Refer to the section 13 for details on the category justification.
Reason / purpose for cross-reference:
read-across source
Reason / purpose for cross-reference:
reference to other study
Principles of method if other than guideline:
A two-year dermal study was conducted in rat to evaluate the carcinogenic potential of the test substance.
GLP compliance:
yes
Limit test:
no
Species:
rat
Strain:
Fischer 344
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Taconic Laboratory Animals and Services, (Germantown, NY)
- Age at study initiation: 6 wk
- Housing: Housed individually in Polycarbonate cages (Lab Products, Inc., Maywood, NJ)
- Bedding: Sani-Chip heat-treated hardwood chips (PJ Murphy Forest Products Corp., Montville, NJ)
- Diet : NIH-07 open formula pelleted diet (Zeigler Brothers, Inc., Gardners, PA), ad libitum
- Water : Tap water (Columbus municipal supply), ad libitum
- Acclimation period: 11 to 12 d

ENVIRONMENTAL CONDITIONS
- Temperature : 20.0-23.9°C
- Humidity : 33-70%
- Air changes : 10/hr
- Photoperiod : 12 h dark/12 h light

IN-LIFE DATES: From: Feb. 1, 1993 To: Jan. 31, 1995
Type of coverage:
open
Vehicle:
ethanol
Details on exposure:
The test substance formulation was applied to the shaved skin of test animals. No further details provided.


Analytical verification of doses or concentrations:
yes
Details on analytical verification of doses or concentrations:
Dose formulations were analysed approximately every 2 months using HPLC. In addition to dose formulation analysis prior to dosing, samples collected after dosing (animal room samples) were analysed periodically. All dose formulations analysed during the 2 year studies were within 10% of the target concentration.
Duration of treatment / exposure:
104 wk
Frequency of treatment:
Five exposures per week
Dose / conc.:
0 mg/kg bw/day (nominal)
Dose / conc.:
50 mg/kg bw/day (nominal)
Remarks:
Corresponding to 85 mg/mL in ethanol
Dose / conc.:
100 mg/kg bw/day (nominal)
Remarks:
Corresponding to 170 mg/mL in ethanol
No. of animals per sex per dose:
50/sex/dose
Control animals:
yes, concurrent vehicle
Details on study design:
Dose selection rationale: Doses of 200 or 400 mg/kg bw/d in the 14 wk study were associated with reduced mean body weights, mild anemia, and significantly increased incidences and severities of lesions of the skin at the site of application. Therefore, these doses were considered inappropriate for a 2-year study. At 100 mg/kg bw/d, the incidences of skin lesions, especially ulceration, were less than at 200 mg/kg bw/d, and in general, the severities were minimal to mild. Therefore, 100 mg/kg bw/d was selected as the high dose for this 2-yr study.
Observations and examinations performed and frequency:
CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Observed twice daily

DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Clinical findings were recorded initially, at 4 wk intervals during the study, and at the end of the study

DERMAL IRRITATION (if dermal study): Yes

BODY WEIGHT: Yes
- Time schedule for examinations: Animals were weighed initially, weekly during week 1 through 13, at 4 wk intervals thereafter, and at the end of the studies


Sacrifice and pathology:
SACRIFICE: Carbon dioxide asphyxiation

GROSS PATHOLOGY: Yes

HISTOPATHOLOGY: Yes, Complete histopathology was performed on all rats. In addition to gross lesions and tissue masses, the following tissues were examined: adrenal gland, bone and marrow, brain, clitoral gland, esophagus, heart, large intestine (cecum, colon, rectum), small intestine (duodenum, jejunum, ileum), kidney, liver, lung, lymph nodes (mandibular and mesenteric), mammary gland, nose, ovary, pancreas, parathyroid gland, pituitary gland, preputial gland, prostate gland, salivary gland, skin, spleen, stomach (forestomach and glandular), testis (and epididymis and seminal vesicle), thymus, thyroid gland, trachea, urinary bladder, and uterus
Statistics:
Survival Analyses: The probability of survival was estimated by the product-limit procedure of Kaplan and Meier (1958). Possible dose-related effects on survival were analysed by Cox’s (1972) method for testing two groups for equality and Tarone’s (1975) life table test to identify dose-related trends. All reported P values for the survival analyses were two-sided.

Analysis of Neoplasm and Nonneoplastic Lesion Incidences: The Poly-k test (Bailer and Portier, 1988; Portier and Bailer, 1989; Piegorsch and Bailer, 1997) was used to assess neoplasm and nonneoplastic lesion prevalence. Tests of significance included pairwise comparisons of each dosed group with controls and a test for an overall dose-related trend. Continuity-corrected tests were used in the analysis of lesion incidence, and reported P values are one sided.

Analysis of Continuous Variables: Organ and body weight data, which historically have approximately normal distributions, were analyzed with the parametric multiple comparison procedures of Dunnett (1955) and Williams (1971, 1972). Jonckheere's test (Jonckheere, 1954) was used to assess the significance of the dose-related trends. Average severity values were analyzed for significance with the Mann-Whitney U test. Treatment effects were investigated by applying a multivariate analysis of variance (Morrison, 1976) to the transformed data to test for simultaneous equality of measurements across dose levels.
Clinical signs:
effects observed, treatment-related
Dermal irritation:
effects observed, treatment-related
Description (incidence and severity):
The only clinical finding attributed to dosing was irritation of the skin at the site of application in 100 mg/kg bw/d females.

Mortality:
mortality observed, treatment-related
Description (incidence):
Survival rates of dosed male and female rats were similar to those of the vehicle controls.
Body weight and weight changes:
no effects observed
Description (incidence and severity):
The mean body weights of dosed male and female rats were similar to those of the vehicle controls throughout the study.

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:
not examined
Urinalysis findings:
not examined
Behaviour (functional findings):
not examined
Organ weight findings including organ / body weight ratios:
no effects observed
Gross pathological findings:
effects observed, treatment-related
Histopathological findings: non-neoplastic:
effects observed, treatment-related
Description (incidence and severity):
Skin: No neoplasms of the skin were attributed to treatment with test material. Incidences of squamous cell papilloma, keratoacanthoma, trichoepithelioma, basal cell adenoma, or carcinoma (combined) were significantly decreased in 100 mg/kg bw/d male rats. Incidences of epidermal hyperplasia, sebaceous gland hyperplasia, parakeratosis, and hyperkeratosis in all dosed groups were significantly greater than those in the vehicle control groups. The severities of these lesions generally increased with increasing dose and ranged from minimal to mild. Females in the 100 mg/kg bw/d group had a significantly greater incidence of ulceration at the site of application than did the vehicle controls.
Histopathological findings: neoplastic:
effects observed, treatment-related
Description (incidence and severity):
Kidney: Incidences of renal tubule hyperplasia in dosed females were significantly greater than those of the vehicle controls, and the incidence of renal tubule adenoma in 50 mg/kg bw/d males was marginally increased. Incidences of chronic nephropathy were similar between vehicle control and dosed groups of male and female rats; however, the severity of nephropathy increased with increasing dose in female rats. The incidences of renal tubule adenoma in all groups of males and of renal tubule carcinoma in 50 mg/kg bw/d females exceeded the historical control ranges. An extended evaluation of the kidney revealed additional renal tubule adenomas in vehicle control and dosed males, and renal tubule adenomas and/or carcinomas in dosed females. When the single and step sections were combined, the incidences of renal tubule hyperplasia in dosed females and of renal tubule adenoma or carcinoma (combined) in 50 mg/kg bw/d females were significantly greater than those of the controls. In female rats, the combined single and step section evaluations of the kidney revealed a significant dose- related increase in the incidence of renal tubule hyperplasia and two adenomas and two carcinomas in the 50 mg/kg bw/d group but only one neoplasm (an adenoma), in the 100 mg/kg bw group. Renal tubule neoplasms are uncommon in female F344/N rats, and the presence of four neoplasms in the 50 mg/kg bw/d group, combined with the increased incidence of hyperplasia, is suggestive of an association with chemical exposure. However, the absence of an increase in neoplasms in the 100 mg/kg bw/d group in the presence of increased hyperplasia makes the association with chemical exposure uncertain.

Forestomach: The incidences of chronic active inflammation (vehicle control, 1/50; 50 mg/kg bw, 3/50; 100 mg/kg bw, 10/50), epithelial hyperplasia (2/50, 5/50, 13/50), and epithelial ulcer (1/50, 3/50, 11/50) were significantly increased in the forestomach of 100 mg/kg bw females. The severities of these lesions were similar among all groups.

Pancreas: The incidence of pancreatic acinar atrophy in 100 mg/kg male rats was significantly greater than that in the vehicle controls.
Key result
Dose descriptor:
NOAEL
Remarks:
(systemic effects)
Effect level:
ca. 50 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
other: pancreatic acinar atrophy and nephropathy at the higher dose
Key result
Dose descriptor:
LOAEL
Remarks:
(local effects)
Effect level:
ca. 50 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
male/female
Basis for effect level:
other: based on non-neoplastic lesions of the skin at all doses
Critical effects observed:
not specified

For detailed tables kindly refer to the attached background materials section of the IUCLID.

Conclusions:
Under the study conditions, the 2-yr NOAEL was considered to be 50 mg/kg bw/day in rat.
Executive summary:

A study was conducted to evaluate the long-term repeated dose dermal toxicity of the read across substance, C8-18 and C18-unsatd. DEA, in compliance with GLP. The experiment was conducted in compliance with GLP. Groups of 50 male and 50 female rats were exposed to 0, 50 or 100 mg/kg bw/day of the substance in ethanol by dermal application, 5 times per week, for 104 weeks. Mortality, clinical signs and bodyweight were recorded throughout the study. At necropsy, a gross macroscopic examination and complete histopathology were carried out. The survival rates of treated male and female rats were similar to those of controls. There were no significant differences in bodyweight throughout the groups. The only treatment-related clinical finding was irritation of the skin at the site of application in 100 mg/kg bw/day females. Non-neoplastic lesions of the skin at the site of application included epidermal hyperplasia, sebaceous gland hyperplasia, parakeratosis and hyperkeratosis, and the incidences and severities of these lesions increased with increasing dose. There were marginal increases in the incidences of renal tubule adenoma or carcinoma (combined) in 50 mg/kg bw/day females. The severity of nephropathy increased with increasing dose in female rats. The incidences of chronic active inflammation, epithelial hyperplasia and epithelial ulcer of the forestomach increased with dose in female rats and the increases were significant in the 100 mg/kg bw/day group. Under the study conditions, there was no evidence of carcinogenic activity of the read across substance in male rats at any dose. There was an equivocal evidence of carcinogenic activity in female rats based on a marginal increase in the incidences of renal tubule neoplasms. However, the absence of an increase in neoplasms in the 100 mg/kg bw/day group in the presence of increased hyperplasia makes the association with treatment uncertain. Under the study conditions, the 2-yr NOAEL was considered to be 50 mg/kg bw/day in rat (Irwin, 2001).

Endpoint conclusion
Endpoint conclusion:
adverse effect observed
Dose descriptor:
NOAEL
50 mg/kg bw/day
Study duration:
chronic
Species:
rat

Repeated dose toxicity: dermal - local effects

Endpoint conclusion
Endpoint conclusion:
no study available

Additional information

Oral (Combined repeated dose and reproductive/developmental screen)


A combined repeated dose toxicity study with the reproduction / developmental toxicity screening was conducted with the read across substance C16-18 and C18-unsatd. DEA in accordance with OECD 422 and in compliance with GLP. Four groups of ten Sprague Dawley rats (males and females) were exposed by oral gavage to increasing concentrations of the test substance (0, 100, 250 and 700 mg/kg/day). All doses were administered at a constant volume of 10 mL/kg body weight. 0.5% aqueous solution of carboxymethylcellulose was used as a vehicle. According to the study design, males were treated for 14 days prior to pairing and during pairing with females until the day before necropsy, for a total of 33/34 days. Females were treated for 14 days prior to pairing, during pairing and throughout the gestation and lactation periods until Day 13 post-partum, for a total of 43 to 63 days. The following investigations were performed: body weight, clinical signs (including neurotoxicity assessment, motor activity and sensory reactivity to stimuli), food consumption, clinical pathology investigations (haematology and clinical chemistry in five randomly selected animals/sex/group), macroscopic observations, organ weights. Routine histopathological examination was performed in control and high dose groups (five randomly selected animals/sex/group). No mortality occurred throughout the study due to the administration of the test substance. Salivation was the only treatment-related clinical sign recorded in males and females treated at 250 and 700 mg/kg/day, during the study. These clinical signs were not considered to be adverse since no effects on the health status were evident in the affected animals. Neurotoxicity assessment (removal from the home cage and observations in an open arena), motor activity, grip strength and sensory reactivity to stimuli did not reveal changes attributable to the test substance. Body weight and body weight gain of treated animals did not show differences throughout the study when compared to the control group. The food consumption was comparable in all groups. No adverse findings were recorded in clinical pathology investigations (haematology including coagulation parameters and clinical chemistry). Hormone analysis did not show any relation to treatment. Urinalysis in male animals did not reveal changes attributable to the test substance. Changes were observed in the stomach of the majority of males and females dosed at 700mg/kg/day at microscopic examination, due to a local irritant effect of the test substance but these signs were not considered to be severe. Under the study conditions, the NOAEL for general toxicity was considered to be 700 mg/kg/day for males and females (Longobardi, 2022).


Oral (90 day)


A study was conducted to evaluate the repeated dose oral toxicity of the read across substance, C12 DEA. The rats were administered read across substance concentrations of 0, 0.1, 0.5, 1 and 2% in diet for 90 d. The animals were observed daily for clinical signs. Body weight were recorded weekly and haematological, clinical chemistry and urine examinations were carried out at termination. Gross and histopathological examinations were also performed at termination. No adverse effect on the appearance or condition of the animals was observed. Growth retardation was associated with diminished food intake from the dose level of 0.5%. Food refusal was demonstrably due to an effect of the test material on palatability of the diet. Terminal haematological examination revealed a reduction in the haemoglobin level, haematocrit and red cell count at the 1 and 2% dose levels in females but less pronounced effects were seen in males. Serum levels of glutamic-oxaloacetic transaminase were elevated at 0.5% and above in females but only at 0.5 % in males. No untoward effect was observed in the renal function tests. The principal organ weight changes were: increases in the relative kidney weight in all test groups except at 0.1% in females and at 0.1 and 0.5% in males, and increases in the relative liver weight in females on the two highest levels. The types and incidence of histological lesions were comparable in control and test groups. Under the study conditions, the 90 d NOEL in rats was considered to be 0.1% in the diet, equivalent to 50 mg/kg bw/day (Gaunt, 1965).


Furthermore, after discussion with ECHA in the frame of a Dossier Improvement Action Plan (DIAP), a testing proposal is submitted for the conduct of repeated dose toxicity study according to OECD Guideline 408 with the read across substance, C8-18 and C18-unsatd. DEA.


Oral (28 day)


A study was conducted to evaluate the repeated dose oral toxicity of the test substance, C12-18 and C18-unsatd. DEA, according to a design based on OECD Guideline 407. Groups of 10 male and 10 female Wistar rats were orally gavaged with the substance diluted in olive oil, 5 d/week for 28 d at doses of 0, 70, 250, 750 (Days 1-14) and 1500 (Days 15-28) mg/kg bw/d. Clinical signs, bodyweight, haematology, clinical chemistry, urinalysis, gross and microscopic pathology were recorded. Additional groups of 5 male and 5 female rats were kept for a 4 month recovery period. No treatment-related adverse effects were observed at any of the doses. Changes in the forestomach at some doses including controls were attributed to the use of olive oil and found to be reversible after end of exposure. Under the study conditions, the 28 d NOAEL to rats was considered to be >750 mg/kg bw/day (Potokar, 1983).


Dermal (14 week)  


A study was conducted to evaluate the repeated dose dermal toxicity of the read across substance, C8-18 and C18-unsatd. DEA, according to a design based on OECD Guideline 411, in compliance with GLP. Groups of 10 male and 10 female B6C3F1mice were exposed to 0, 50, 100, 200, 400 or 800 mg/kg bw/day of the substance in ethanol by dermal application, 5 times per week, for 14 weeks. Mortality, clinical signs and bodyweight were recorded throughout the study. At the end of the study, samples were collected for sperm motility and vaginal cytology evaluations in the 0, 200, 400 and 800 mg/kg bw/day dose groups. At necropsy, a gross macroscopic examination was conducted. Selected organs were weighed and a complete histopathological evaluation was carried out for 0 and 800 mg/kg bw/day mice. All mice survived until the end of the study. The only treatment related clinical finding was irritation of the skin at the site of application in males and females administered 800 mg/kg bw/day. There were no effects on body weight. Weights of the liver and kidney of 800 mg/kg bw/day males and females, liver of 400 mg/kg bw/day females and lung of 800 mg/kg bw/day females were significantly increased compared to the controls. Epididymal spermatozoa concentration was significantly increased in 800 mg/kg bw/day males. Histopathologic lesions of the skin at the site of application included epidermal hyperplasia, sebaceous gland hyperplasia, chronic active inflammation, parakeratosis and ulcer. The incidences and severities of these skin lesions generally increased with increasing dose in males and females. Under the study conditions, the 14-week NOAEL in mice for systemic effects was considered to be 200 mg/kg bw/day and for the local effects 100 mg/kg bw/day (Irwin, 2001).  


A study was conducted to evaluate the repeated dose toxicity of the read across substance, C8-18 and C18-unsatd. DEA, according to a design based on OECD Guideline 411, in compliance with GLP. Groups of 10 male and 10 female Fischer 344 rats were exposed to 0, 25, 50, 100, 200 or 400 mg/kg bw/day of the substance in ethanol by dermal application, 5 times per week, for 14 weeks. Mortality, clinical signs and bodyweight were recorded throughout the study. Blood was collected on days 4 and 24 for hematology and clinical chemistry analysis. At the end of the study, samples were collected for sperm motility and vaginal cytology evaluations in the 0, 100, 200 or 400 mg/kg bw/day dose groups. At necropsy, a gross macroscopic examination was conducted. Selected organs were weighed and a complete histopathological evaluation was carried out for 0 and 400 mg/kg/day rats. All rats survived until the end of the study. Clinical findings included irritation of the skin at the site of application in 100, 200 and 400 mg/kg bw/day males and females. Final mean bodyweights and bodyweight gains of 200 and 400 mg/kg bw/day males and females were significantly lower than those of the controls. At week 14, a minimal microcytic, normochromic, non-responsive anaemia occurred in the 100 and 200 mg/kg bw/day females and 400 mg/kg bw/day males and females. The anaemia was also seen in the 400 mg/kg bw/day males and females on day 24. Increased segmented neutrophil counts occurred in 400 mg/kg bw/day males and females at week 14 and in 400 mg/kg bw/day females on day 24. Cholesterol concentrations were significantly decreased in 200 and 400 mg/kg bw/day males and in females administered 100 mg/kg bw/day or greater. Triglyceride concentrations were decreased in 200 and 400 mg/kg bw/day males. Histopathological lesions of the skin at the site of application included epidermal hyperplasia, sebaceous gland hyperplasia, chronic active inflammation, parakeratosis and ulcer. The incidence and severity of these skin lesions generally increased with increasing dose in males and females. The incidences of renal tubule regeneration in 100, 200 and 400 mg/kg bw/day females were significantly greater than in controls, and the severity in 200 and 400 mg/kg bw/day females was increased. Under the study conditions, the 14-week systemic NOAEL in rats was considered to be 50 mg/kg bw/day (Irwin, 2001). 


Dermal (2 year) 


A study was conducted to evaluate the long-term repeated dose dermal toxicity to B6C3F1 mice of the read across substance, C8-18 and C18-unsatd. DEA, in compliance with GLP. The doses studied included 0, 100 and 200 mg/kg bw/day of read across substance (corresponding to 0, 50, or 100 mg/mL in ethanol). Fifty male/female test animals were used in each group. Five exposures per week were administered for 104 to 105 weeks. The animals were observed twice daily, and body weights and clinical findings were recorded periodically. All animals were necropsied and complete histopathology was performed. Survival of dosed male and female mice was generally similar to that of the vehicle controls. The mean bodyweights of the 100 mg/kg bw/day females from week 93 and of the 200 mg/kg bw/day females from week 77 were lower than those of the vehicle controls. The only clinical finding attributed to treatment was an irritation of the skin at the site of application in males administered 200 mg/kg bw/day. The incidences of hepatic neoplasms (hepatocellular adenoma, hepatocellular carcinoma and hepatoblastoma) were significantly increased in male and/or female mice. The number of eosinophilic foci in dosed groups of male mice was higher than in the vehicle controls. The occurrences of renal tubule adenoma and renal tubule adenoma or carcinoma (combined) were significantly increased in 200 mg/kg bw/day males. Several non-neoplastic lesions of the skin at the site of application were considered treatment-related. Incidences of epidermal hyperplasia, sebaceous gland hyperplasia and hyperkeratosis were greater in all dosed groups than in the vehicle controls and the number of thyroid gland follicular cell hyperplasia in all dosed groups was also significantly greater than those in the vehicle control groups. There was clear evidence of carcinogenic activity in male B6C3F1 mice based on increased incidences of hepatic and renal tubule neoplasms and in female B6C3F1 mice based on increased incidences of hepatic neoplasms. These increases were associated with the concentration of free diethanolamine present as a contaminant in the read across substance. However, recent evidences suggest that DEA should not be classified as a carcinogen, as the hepatic tumours seen in mice and the proposed mode of non-genotoxic mechanism for renal/liver tumours are not relevant to humans/primates. Under the study conditions, the 2-yr LOAEL was considered to be 100 mg/kg bw/day in mouse (Irwin, 2001).  


A study was conducted to evaluate the long-term repeated dose dermal toxicity to Fischer 344 rats of the read across substance, C8-18 and C18-unsatd. DEA, in compliance with GLP. Groups of 50 male and 50 female rats were exposed to 0, 50 or 100 mg/kg bw/day of the substance in ethanol by dermal application, 5 times per week, for 104 weeks. Mortality, clinical signs and bodyweight were recorded throughout the study. At necropsy, a gross macroscopic examination and complete histopathology were carried out. The survival rates of treated male and female rats were similar to those of controls. There were no significant differences in bodyweight throughout the groups. The only treatment-related clinical finding was irritation of the skin at the site of application in 100 mg/kg bw/day females. Non-neoplastic lesions of the skin at the site of application included epidermal hyperplasia, sebaceous gland hyperplasia, parakeratosis and hyperkeratosis, and the incidences and severities of these lesions increased with increasing dose. There were marginal increases in the incidences of renal tubule adenoma or carcinoma (combined) in 50 mg/kg bw/day females. The severity of nephropathy increased with increasing dose in female rats. The incidences of chronic active inflammation, epithelial hyperplasia and epithelial ulcer of the forestomach increased with dose in female rats and the increases were significant in the 100 mg/kg bw/day group. Under the study conditions, there was no evidence of carcinogenic activity of the read across substance in male rats at any dose. There was an equivocal evidence of carcinogenic activity in female rats based on a marginal increase in the incidences of renal tubule neoplasms. However, the absence of an increase in neoplasms in the 100 mg/kg bw/day group in the presence of increased hyperplasia makes the association with treatment uncertain. Under the study conditions, the 2-yr NOAEL was considered to be 50 mg/kg bw/day in rat (Irwin, 2001).


Additional considerations


Based on an in-depth analysis of the available information (see read-across justification in Section 13 of the IUCLID dataset), it is the hypothesis that a read-across within and across MEA, DEA and MIPA derived alkanolamides is scientifically plausible and justified. While there is at present no evidence for putting the read-across hypothesis in question, some limitations, predominantly related to the quality of individual endpoint studies (including quality of the test substance characterisations) and existing higher tier endpoint data gaps, are recognized. Accordingly, additional physico-chemical and toxicology data were generated in Tier 1 of a tiered testing programme to strengthen the toxicokinetic and toxicological link within and across the members of the DEA, MEA, and MIPA subcategories.


In Tier 1, a series of bridging studies according to OECD TG 421 and 422 were conducted with a representative short- and a long-chain substance of each subcategory (i.e., DEA, MEA, and MIPA). Additionally, taking advantage of the bridging studies samples, metabolomics analyses were conducted to enhance the quality and quantity of data from a biological perspective.


Overall, the results of the Tier 1 testing confirmed and supported the hypothesis of a similar toxicological profile within and across the different sub-categories. All investigated substances displayed in line with existing data a similar systemic toxicity profile with no observed repeated dose toxicity at the highest tested dose (i.e., NOAELs ≥ 700 mg/kg/day) and absence of reproductive or developmental toxicity. The absence of significant metabolome changes is in line with the Tier 1 in vivo findings, and thereby further confirming the read-across hypothesis that there is no significant difference in terms of type and strength of effects within and across the FAA subcategories.


In the present dossier update, proposed Tier 2 studies have been included with the aim to generate a complete set of higher toxicology data for a selected >1000 tpa substance (i.e., OECD TG 408/443/414 (rats)/414 (2nd species). The testing in Tier 2 will be conducted with C8-18 and C18-unsatd. DEA, the substance that is generally perceived to be the most critical from a toxicological point of view due to the proposed hazard classification of DEA. Additionally, a few minor non-significant metabolomic changes were noted for the investigated DEA-FAA substance (i.e., C16-18 and C18-unsatd. DEA), suggesting some type of biological activity, possibly explaining some findings in the 1000 mg/kg bw/day dose group in the dose-range finding study. These observations support the selection and recommendation to investigate a DEA-FAA substance as a 'worst case' for the FAA category in Tier 2.


The strategy and status overview are detailed in the document entitled ‘ECHA-DIAP - FAA testing strategy summary status overview – Oct 22’, attached in Section 13 of the IUCLID dataset.

Justification for classification or non-classification

Based on the results of oral and dermal repeated dose toxicity studies in rodents with the substance itself or the read across substances C16-18 and C18-unsatd. DEA, C12 DEA or C8-18 and C18-unsatd. DEA, the test substance does not require classification for this endpoint according to CLP (EC 1272/2008) criteria.