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EC number: 208-686-5 | CAS number: 538-23-8
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Carcinogenicity
Administrative data
Description of key information
Oral (2-year oral gavage study): NOAEL male rat: 2390 mg/kg bw/day
Key value for chemical safety assessment
Carcinogenicity: via oral route
Link to relevant study records
- Endpoint:
- carcinogenicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- Acceptable, well documented technical report which meets basic scientific principles.
- Reason / purpose for cross-reference:
- reference to same study
- Principles of method if other than guideline:
- Male rats were exposed to corn oil, safflower oil and tricaprylin via gavage. After 15 months (interim evaluation) and 2 years, animals were sacrificed for gross and histopathological examinations to evaluate the treatment-related effects on neoplasm incidence.
- GLP compliance:
- yes
- Species:
- rat
- Strain:
- other: Fischer 344/N
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Simonsen Laboratories (Gilroy, CA)
- Age at study initiation: 7 weeks
- Weight at study initiation: 126 - 159 g (range)
- Housing: groups of 5 animals in polycarbonate cages with hardwood chips
- Diet: NIH-07 open-stock mash diet (Zeigler Bros., Inc., Gardners, PA), ad libitum
- Water: Worcester public water, ad libitum
- Acclimation period: 14 to 22 days; prior to study start, five rats from each study were randomly selected and killed for parasite evaluation and gross observation of disease.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21-22
- Humidity (%): 47.1 ± 4.9
- Air changes (per hr): at least 10
- Photoperiod (hrs dark / hrs light): 12/12 - Route of administration:
- oral: gavage
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS:
Tricaprylin was dispensed into vials for gavage dosing on a weekly basis. After dispensing, the test item was stored at 4°C for no more than 3 weeks. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Accelerated bulk chemical stability studies were performed using gas chromatography. The test substance was found to be stable as a bulk chemical for 2 weeks when stored protected from light at temperatures up to 60°C. The stability of tricaprylin was monitored periodically by ultraviolet spectroscopy and gas chromatography. In addition, the peroxide concentration was determined prior to use. The acceptable peroxide concentration was set at 2 mEq/L. A bottle was discareded if it exceeded this specification. No significant degradation of the bulk chemical was observed throughout the study.
- Duration of treatment / exposure:
- 24 months (50 males per group)
15 months (10 males per group, interim group) - Frequency of treatment:
- daily; 5 days/week
- Post exposure period:
- None
- Dose / conc.:
- 2 390 mg/kg bw/day (actual dose received)
- Remarks:
- 2.5 mL/kg bw/day, dose calculated based on a density of 0.9540 g/cm³
- Dose / conc.:
- 4 770 mg/kg bw/day (actual dose received)
- Remarks:
- 5 mL/kg bw/day, dose calculated based on a density of 0.9540 g/cm³
- Dose / conc.:
- 9 540 mg/kg bw/day (actual dose received)
- Remarks:
- 10 mL/kg bw/day, dose calculated based on a density of 0.9540 g/cm³
- No. of animals per sex per dose:
- 60 males/group; 10 from each group were sacrificed after 15 months
- Control animals:
- yes, concurrent no treatment
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: twice daily, findings were recorded at least monthly
BODY WEIGHT: Yes
- Time schedule for examinations: at study initiation, than weekly for 13 weeks, and monthly thereafter
HAEMATOLOGY: Yes
- Time schedule for collection of blood: at 15 months. Blood was collected from the posterior vena cava.
- How many animals: 10
- Parameters checked: haematocrit, haemoglobin, erythrocyte count, mean erythrocyte haemoglobin, mean erythrocyte haemoglobin concentration, mean erythrocyte haemoglobin volume, reticulocyte count, total and differential leukocyte count
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: at 15 months from the posterior vena cava
- How many animals: 10
- Parameters checked: potassium, total protein, albumin, cholesterol, alanine aminotransferase, creatine kinase, sorbitol dehydrogenase, bile acids - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes, on all animals. Animals found in a moribund state, selected for the 15-month interim evaluations, or surviving to the end of the 2-year study were killed by the use of "Biotol", an ultra fast-acting barbiturate. All organs and tissues were examined for gross lesions.
HISTOPATHOLOGY: Yes, on all animals. All of the following tissues were preserved in 10% neutral puffered formalin, embedded in paraffin, sectioned, and stained with hematoxylin and eosin for microscopic examination: Adrenal gland, bone and marrow, brain, esophagus, gross lesions, heart, kidney, large intestine (cecum, colon, rectum), liver, lung, mammary gland, lymph nodes (mandibular and mesenteric), pancreas, parathyroid gland, pituitary gland, preputial gland, salivary gland, skin, small intestine (duodenum, jejunum, ileum), spleen, stomach, testis with epididymis and seminal vesicle, thymus, thyroid gland, tissue masses, trachea, and urinary bladder. - Other examinations:
- Brain, kidney (right) and liver of each animal were weighed at the 15 month interim evaluation.
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- 9540 mg/kg bw/day: Clinical findings including dyspnoea, ataxia and lethargy were observed in 50/60 animals in the high-dose group. However, most of the animals generally recovered prior to the next daily dosing and the incidence of clinical findings declined during the second half of the study.
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- 9540 mg/kg bw/day: 30 animals died, other group: comparable survival rats
The two-year survival rate was lower in test animals compared with the untreated controls with statistical significance for the high-dose group only (31/50, 30/50, 31/50, 23/53 for control, 2390, 4770, 9540 mg/kg bw/day, respectively (Table 1)). Twenty-three rats of the high-dose group died or were killed between weeks 33 and 85. Ten of these animals were found dead and 13 were killed moribund. Although the cause of death or moribund condition could not-be-determined in 20 of these animals, clinical findings were noted in all of the moribund animals. Of these, eight rats died or were killed between weeks 45 and 49, when the incidence of clinical findings was highest. The average body weight of these eight animals was 316 g, which was significantly less than the mean group body we
ight of approximately 360 g for high-dose group at 11 months. Only one of the moribund animals had a pulmonary mass that might have explained the dyspnoea. Up to four animals in the high-dose group died or were killed in each subsequent month. - Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- 9540 mg/kg bw/day: Mean body weights were decreased in test animals compared to controls throughout the study. However, the difference was less than 5% after week 61. No effects were observed in the low- and mid-dose group.
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- A dose-dependent decrease in food consumption was determined in test animals (table 3) which resulted in a decreased protein consumption per day (protein consumption (g/rat/day): 3.88, 3.45, 3.09 and 2.70, for control, low-, mid- and high-dose animals, respectively). This effect is most probably due to the fact that rats exposed to tricaprylin received more than 10% of their caloric intake from the test item (10.4%, 19.8% and 35.4% for the low-, mid- and high-dose animals, respectively). Thus, the effect on food consumption is considered as non-adverse.
- 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):
- Significant increases in the haematocrit, haemoglobin and erythocyte counts were determined for the high-dose group. No effects were observed in the low- and mid-dose group.
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Test animals of the mid-dose group revealed a statistically significant lower absolute kidney weight. As the relative organ weight is not different from the control and the effect is not observed in the low- and high-dose group, the effect is considered as incidental and not treatment-related.
- Gross pathological findings:
- no effects observed
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- no effects observed
- Description (incidence and severity):
- No adverse effects observed.
A significant decrease in the incidence of nephropathy was determined in the high-dose group (control: 46/50, 2390 mg/kg bw/day: 42/50, 4770 mg/kg bw/day: 45/50, 9540 mg/kg bw/day: 27/49) with a dose-related decrease in severity (control: 2.0, 2390 mg/kg bw/day: 1.5, 4770 mg/kg bw/day: 1.7, 9540 mg/kg bw/day: 0.9). As the severity of nephropathy is normally related to the amount of protein in the diet, the decrease in severity induced by tricaprylin might be due to the lower food consumption in test animals. No further findings have been determined in control vs test animals. - Histopathological findings: neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- dose-related increase in the incidences of pancreatic exocrine hyperplasia and adenoma; proliferative lesions of the forestomach.
Tricaprylin induced dose-related increases in the tumor incidences of pancreatic exocrine hyperplasia reaching statistically significance for the mid-and high-dose group (control: 8/49, 2390 mg/kg bw/day: 9/49, 4770 mg/kg bw/day: 18/49, 9540 mg/kg bw/day: 28/50), adenoma (control: 2/49, 2390 mg/kg bw/day: 6/49, 4770 mg/kg bw/day: 13/49, 9540 mg/kg bw/day: 18/50) and proliferative lesions in the forestomach (basal cell hyperplasia: control: 4/50, 2390 mg/kg bw/day: 7/50, 4770 mg/kg bw/day: 12/49, 9540 mg/kg bw/day: 21/52; squamous cell papilloma: control: 0/50, 2390 mg/kg bw/day: 0/50, 4770 mg/kg bw/day: 3/50, 9540 mg/kg bw/day: 10/53) reaching statistically significance for squamous cell papilloma in the high-dose group. In contrast, a decrease in the incidence of mononuclear cell leukemia was observed in high-dose animals (control: 23/50, 2390 mg/kg bw/day: 28/50, 4770 mg/kg bw/day: 22/50, 9540 mg/kg bw/day: 9/53). The incidence of pancreatic islet hyperplasia and adenoma or carcinoma decreased in a dose-dependent, but not significant manner (hyperplasia: control: 6/49, 2390 mg/kg bw/day: 5/48, 4770 mg/kg bw/day: 3/49, 9540 mg/kg bw/day: 1/49; adenoma/carcinoma: control: 5/49, 2390 mg/kg bw/day: 2/48, 4770 mg/kg bw/day: 3/49, 9540 mg/kg bw/day: 1/49) - Key result
- Dose descriptor:
- NOAEL
- Remarks:
- carcinogenicity
- Effect level:
- 2 390 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Key result
- Dose descriptor:
- LOAEL
- Remarks:
- carcinogenicity
- Effect level:
- 4 770 mg/kg bw/day (actual dose received)
- Based on:
- test mat.
- Sex:
- male
- Basis for effect level:
- histopathology: neoplastic
- Key result
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 4 770 mg/kg bw/day (actual dose received)
- System:
- gastrointestinal tract
- Organ:
- pancreas
- Treatment related:
- yes
- Dose response relationship:
- yes
- Relevant for humans:
- yes
- Key result
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 4 770 mg/kg bw/day (actual dose received)
- System:
- gastrointestinal tract
- Organ:
- other: forestomach
- Treatment related:
- yes
- Dose response relationship:
- yes
- Relevant for humans:
- no
- Conclusions:
- A statistically significant dose-related increase in pancreatic acinar cell hyperplasia and adenoma was found, but there were no acinar carcinomas. The incidence of mononuclear leukemia was less, and nephropathy findings were reduced. No level of evidence of carcinogenicity was assigned by the study authors.
Reference
Table 1: Mortality data after tricaprylin exposure
|
control |
2390 mg/kg bw/day |
4770 mg/kg bw/day |
9540 mg/kg bw/day |
number of animals included in the study |
60 |
60 |
60 |
60 |
sacrificed for 15-month interim evaluationa |
10 |
10 |
10 |
7 |
natural deaths |
4 |
7 |
4 |
13 |
moribund kills |
15 |
13 |
15 |
17 |
animals surviving until study termination |
31d |
30 |
31d |
23d |
mean survival (days)b |
651 |
639 |
642 |
553 |
survival analysisc |
P = 0.004 |
P = 0.944 |
P = 0.969 |
P = 0.014 |
a: censored from survival analyses
b: mean of all death including uncensored, censored and terminal sacrifice
c: The result of the life table trend test (Tarone, 1975) is shown in the control column whereas the results of life table pairwise comparisons (Cox, 1972) with the controls are listed in the dosage columns.
d: Includes 2 rats for the control and 1 rat for the mid- and high-dose groups that died during the last week of the study.
Table 2: Effects on body weight after tricaprylin exposure
|
body weight (g) |
|||
weeks on study |
control |
2390 mg/kg bw/day |
4770 mg/kg bw/day |
9540 mg/kg bw/day |
1 |
146 |
144 |
145 |
145 |
2 |
172 |
171 |
169 |
168 |
3 |
199 |
198 |
193 |
190 |
4 |
219 |
215 |
215 |
207 |
5 |
243 |
241 |
239 |
231 |
7 |
263 |
259 |
255 |
247 |
8 |
266 |
265 |
257 |
254 |
9 |
283 |
282 |
277 |
266 |
10 |
300 |
295 |
285 |
278 |
12 |
306 |
301 |
294 |
283 |
13 |
306 |
301 |
296 |
284 |
14 |
317 |
311 |
303 |
289 |
17 |
332 |
329 |
319 |
303 |
21 |
351 |
350 |
339 |
319 |
25 |
363 |
367 |
354 |
330 |
29 |
376 |
372 |
357 |
335 |
33 |
381 |
379 |
371 |
345 |
37 |
386 |
387 |
376 |
353 |
41 |
388 |
389 |
377 |
347 |
45 |
389 |
389 |
382 |
358 |
49 |
388 |
395 |
388 |
368 |
53 |
401 |
408 |
396 |
380 |
57 |
404 |
411 |
394 |
380 |
61 |
403 |
416 |
400 |
390 |
65 |
408 |
419 |
399 |
392 |
69a |
406 |
421 |
400 |
392 |
73 |
408 |
422 |
403 |
395 |
77 |
414 |
423 |
406 |
403 |
81 |
413 |
419 |
405 |
404 |
85 |
405 |
412 |
396 |
399 |
89 |
402 |
412 |
390 |
395 |
93 |
400 |
413 |
393 |
397 |
97 |
393 |
406 |
386 |
391 |
101 |
387 |
404 |
379 |
379 |
104 |
386 |
391 |
371 |
366 |
mean (week 1–13) |
246 |
243 |
239 |
232 |
mean (week 14–52) |
367 |
367 |
357 |
335 |
mean (week 53–104) |
402 |
413 |
394 |
390 |
a: interim evaluation occurred during week 67
Table 3: Effects on food consumption after tricaprylin exposure
|
food consumption per animal per day (g) |
|||
weeks on study |
control |
2390 mg/kg bw/day |
4770 mg/kg bw/day |
9540 mg/kg bw/day |
2 |
14.2 |
13.7 |
12.5 |
11.4 |
5 |
16.9 |
15.9 |
16.0 |
14.4 |
9 |
17.1 |
16.5 |
16.4 |
13.6 |
13 |
13.0 |
12.1 |
9.9 |
8.9 |
17 |
20.2 |
16.9 |
16.0 |
13.5 |
21 |
15.8 |
14.9 |
12.5 |
10.0 |
25 |
18.3 |
18.3 |
16.5 |
13.5 |
29 |
17.8 |
16.2 |
14.0 |
12.2 |
33 |
17.8 |
16.3 |
16.0 |
13.7 |
37 |
18.3 |
15.6 |
14.2 |
12.1 |
41 |
15.2 |
12.8 |
11.5 |
8.8 |
45 |
16.7 |
14.9 |
12.5 |
10.8 |
49 |
20.3 |
17.7 |
15.8 |
13.3 |
53 |
18.2 |
16.2 |
14.2 |
12.1 |
57 |
20.4 |
17.5 |
14.1 |
12.7 |
61 |
17.9 |
16.5 |
14.2 |
12.5 |
65 |
16.8 |
13.7 |
11.9 |
10.6 |
69 |
18.6 |
17.3 |
16.5 |
15.6 |
73 |
16.8 |
14.1 |
12.9 |
10.2 |
77 |
17.7 |
14.3 |
12.9 |
11.2 |
81 |
17.7 |
14.5 |
13.2 |
10.7 |
85 |
15.9 |
14.3 |
12.2 |
10.3 |
89 |
13.9 |
12.6 |
10.6 |
9.5 |
93 |
16.6 |
14.4 |
15.9 |
15.1 |
97 |
16.5 |
12.3 |
12.3 |
12.9 |
101 |
13.7 |
12.3 |
9.4 |
8.7 |
104 |
13.5 |
10.6 |
9.2 |
7.6 |
mean |
17.0 |
15.1 |
13.6 |
11.8 |
Table 4: Haematology data after tricaprylin exposure at the 15-month interim evaluation
|
control |
2390 mg/kg bw/day |
4770 mg/kg bw/day |
9540 mg/kg bw/day |
number of animals |
9 |
10 |
8 |
7 |
haematocrit (%) |
45.6 ± 1.1 |
50.7 ± 2.7 |
49.2 ± 2.3 |
51.7 ± 2.0* |
haemoglobin (g/dL) |
15.6 ± 0.4 |
17.3 ± 0.8 |
16.7 ± 0.6 |
17.5 ± 0.6* |
erythrocytes (106/ µL) |
8.77 ± 0.31 |
9.72 ± 0.41 |
9.30 ± 0.34 |
9.91 ± 0.32* |
*: significantly different from control by Dunn´s or Shirley´s test (P ≤ 0.05)
Table 5: Organ weights of the kidney (right) after tricaprylin exposure at the 15-month interim evaluation
|
control |
2390 mg/kg bw/day |
4770 mg/kg bw/day |
9540 mg/kg bw/day |
number of animals |
10 |
10 |
10 |
7 |
body weight at necropsy |
430 ± 15 |
419 ± 11 |
402 ± 15 |
406 ± 12 |
absolute |
1.349 ± 0.04 |
1.23 ± 0.036 |
1.194 ± 0.041* |
1.328 ± 0.053 |
relative |
3.15 ± 0.07 |
2.95 ± 0.07 |
2.98 ± 0.07 |
3.27 ± 0.08 |
*: significantly different from the control by William´s or Dunnett´s test (P ≤ 0.05)
Organ weights are given in grams; organ-weight-to body-weight ratios are given as mg organ/g bw
Table 6: Histopathological findings after tricaprylin exposure
|
Untreated control |
2390 mg/kg bw/day |
4770 mg/kg bw/ day |
9540 mg/kg bw/day |
|
nephropathy incidence |
46/50 (92%) |
42/50 (84%) |
45/50 (90%) |
27/49 (55%)* |
|
nephropathy severity grade |
2.0 ± 0.12 |
1.5 ± 0.13** |
1.7 ± 0.11* |
0.9 ± 0.13** |
|
forestomach: basal cell hyperplasia |
4/50 |
7/50 |
12/49 |
21/52 |
|
mononuclear cell leukemia (trend test) |
23/50 (46%) p=0.029 |
28/50 (56%) p=0.205 |
22/50 (44%) p=0.525 |
9/53 (17%) p=0.071 |
|
pancreatic islet hyperplasia |
6/49 |
5/48 |
3/49 |
1/49 |
|
pancreatic islet adenoma/carcinoma |
5/49 |
2/48 |
3/49 |
1/49 |
* Significantly different (p≤0.05) from the control group by the logistic regression test (overall rate) or the Mann-Whitney U test (severity)
**p≤0.01
Average severity grade is given as mean f standard error. 0 = none, 1 = minimal, 2 = mild, 3 = moderate, and 4 = marked
Table 7: Incidences of Proliferative Lesions of the Exocrine Pancreas
|
Untreated Control |
2390 mg/kg bw/day |
4770 mg/kg bw/day |
9540 mg/kg bw/day |
Hyperplasia -overall rate |
8/49 (16%) |
9/49 (18%) |
18/49 (37%)* |
28/50 (56%)** |
Adenoma – overall rate |
2/49 (4%) |
6/49 (12%) |
13/49 (27%) |
18/50 (36%) |
Adenoma – terminal rate |
2/30 (7%) |
6/30 (20%) |
11/31 (35%) |
16/23 (70%) |
First incidence (days) |
729 (terminal sacrifice) |
729 (terminal sacrifice) |
518 |
485 |
Logistic regression test |
p<0.001 |
p=0.129 |
p=0.002 |
p<0.001 |
*Significantly different (p≤0.05) from the control group by the logistic regression test
**p≤0.01
Beneath the control incidence are the p values associated with the trend test. Beneath the dosed group incidences are the p values corresponding to pairwise comparisons between the controls and that dosed group. The logistic regression test regards neoplasms as nonfatal.
Table 8 Incidences of Squamous Cell Papilloma (Neoplasms of the Forestomach)
|
Untreated Control |
2390 mg/kg bw/day |
4770 mg/kg bw/day |
9540 mg/kg bw/day |
Overall rate |
0/50 (0%) |
0/50 (0%) |
3/50 (6%) |
10/53 (19%) |
First incidence (days) |
- |
- |
623 |
623 |
Logistic regression test |
p<0.001 |
- |
p=0.118 |
p<0.001 |
Beneath the control incidence is the p value associated with the trend test. Beneath the dosed group incidence are the p values corresponding to pairwise comparisons between the controls and that dosed group. The logistic regression test regards neoplasms as nonfatal.
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 2 390 mg/kg bw/day
- Study duration:
- chronic
- Species:
- rat
- Quality of whole database:
- The available information comprise an adequate and reliable (Klimisch score 2) study with the target substance.
- System:
- gastrointestinal tract
- Organ:
- pancreas
Carcinogenicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Mode of Action Analysis / Human Relevance Framework
Not applicable.
Justification for classification or non-classification
The available data on carcinogenicity are inconclusive according to Regulation (EC) 1272/2008.
Additional information
Repeated dose toxicity, 2-year oral gavage study
CAS 538-23-8
The chronic oral toxicity of glycerol trioctanoate (CAS 538-23-8), also named tricaprylin, was investigated in male F344/N rats in comparison to corn oil and safflower oil (key, 1994). The National Toxicology Program (NTP) designed studies to evaluate the role of several oils in altering cancer rates in male rats. Control male rats receiving corn oil (often used as vehicle) have previously been shown to have a higher incidence of pancreatic proliferative lesions and a lower incidence of mononuclear cell leukaemia than untreated control males. To evaluate 3 gavage vehicles for potential systemic toxicity and carcinogenicity, corn oil, safflower oil, and tricaprylin (CAS 538-23-8) were administered by gavage to male F344/N rats for 2 years. Sixty animals per dose were administered tricaprylin at 2.5, 5 or 10 mL/kg bw once daily for 5 days per week by oral gavage. The doses were equivalent to 2390, 4770 and 9540 mg/kg bw/day as calculated using a density of 0.954 g/cm³. Sixty control animals remained untreated.
All non-neoplastic study results (including clinical signs and mortality) are summarized under the endpoint repeated dose toxicity. In high-dose animals a decrease in the incidence of mononuclear cell leukaemia was observed; this is not considered to have toxicological significance. Proliferative lesions of the forestomach (basal cell hyperplasia, squamous cell papilloma) were seen in the mid- and high-dose groups. These are considered to be treatment-related, but are most likely not relevant for humans as humans do not have a forestomach. A dose-dependent increase in the incidence of proliferative lesions of the exocrine pancreas (hyperplasia and adenoma) was seen; the overall rates were statistically significant in the mid- and high-dose group. The mechanism by which dietary fats or triglycerides stimulate proliferation of the exocrine pancreas in the rat is unclear, but the effect has been reported in public literature. No pancreatic carcinoma was observed in rats given glycerol trioctanoate in this study. Based on the high doses administered to rats over 2 years via oral gavage, the absence of pancreatic carcinoma in this study and the establishment of a NOAEL, no clear evidence of genotoxic carcinogenicity is shown for glycerol trioctanoate (CAS 538-23-8). The NOAEL for non-genotoxic carcinogenicity was found to be 2390 mg/kg bw/day based on the study results.
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