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EC number: 217-164-6 | CAS number: 1760-24-3
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Repeated dose toxicity: inhalation
Administrative data
- Endpoint:
- sub-chronic toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 23 February 2017 to December 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- ECHA decision number: TPE-D-2114300905-56-01/F
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 017
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 413 (Subchronic Inhalation Toxicity: 90-Day Study)
- Deviations:
- not specified
- Remarks:
- There are no deviations from the test guideline that affect the integrity of the study
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- N-(3-(trimethoxysilyl)propyl)ethylenediamine
- EC Number:
- 217-164-6
- EC Name:
- N-(3-(trimethoxysilyl)propyl)ethylenediamine
- Cas Number:
- 1760-24-3
- Molecular formula:
- C8H22N2O3Si
- IUPAC Name:
- N-(3-(trimethoxysilyl)propyl)ethylenediamine
Constituent 1
- Specific details on test material used for the study:
- STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: In a room with controls set to maintain 18°C to 24°C and under dry nitrogen gas, keep away from moisture with dessicant.
- Stability under test conditions: The test article is considered to be stable.
- Solubility and stability of the test substance in the solvent/vehicle: Filtered air was used as vehicle.
- Reactivity of the test substance with the solvent/vehicle of the cell culture medium: not applicable
TREATMENT OF TEST MATERIAL PRIOR TO TESTING
- Treatment of test material prior to testing: not applicable
- Preliminary purification step (if any): not applicable
- Final dilution of a dissolved solid, stock liquid or gel: not applicable
- Final preparation of a solid: not applicable
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Remarks:
- Crl: CD(SD)
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Laboratories
- Females (if applicable) nulliparous and non-pregnant: yes
- Age at study initiation: approximately 7 weeks
- Weight at study initiation: 227 to 307 g (males)/149 to 192 g (females)
- Fasting period before study: Food and water were not available during the exposure period.
- Housing: All animals were housed in groups of 2 to 4 per cage following receipt in clean, solid bottom cages with bedding material.
- Diet: PMI Nutrition International, LLC Certified Rodent LabDiet® 5002 meal was available ad libitum
- Water: Reverse osmosis-treated water was available ad libitum
- Acclimation period: 14 days
DETAILS OF FOOD AND WATER QUALITY: Filters servicing the automatic watering system were changed regularly according to SOPs. The municipal water supplying the laboratory was analyzed for contaminants according to SOPs. SOPs provide specifications for acceptable levels of heavy metals and pesticides that are reasonably expected to be present in the diet without interfering with the purpose or conduct of the study. No contaminants were reasonably expected to be present in water or diet that would interfere with the objectives of the study, therefore, no testing was conducted as part of the study.
ENVIRONMENTAL CONDITIONS
- Temperature (°F): 20°C and 26°C
- Humidity (%): 15-30%
- Air changes (per hr): 10 per hour
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- inhalation: aerosol
- Type of inhalation exposure:
- nose only
- Vehicle:
- air
- Mass median aerodynamic diameter (MMAD):
- > 1.3 - <= 2.1 µm
- Geometric standard deviation (GSD):
- 2.47
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: stainless steel, conventional nose-only exposure systems
- Method of holding animals in test chamber: nose-only exposure restraint tubes
- Source and rate of air:
- Method of conditioning air:
- System of generating particulates/aerosols: Liquid droplet aerosol atmospheres of the test substance were generated using single-jet Collision nebulizers. Test substance exposure atmospheres were generated by mixing the aerosolized test substance with nitrogen and/or breathing-quality dry, compressed air in the appropriate ratio to achieve the target concentrations. Specific exposure atmosphere generation equipment, operating parameters and methods were defined during method development.
- Temperature, humidity, pressure in air chamber: Average daily temperature and relative humidity of the exposure atmospheres were 23 ± 3ºC and 15%-30%, respectively. Temperature and relative humidity were monitored continuously and recorded at approximately 60-minute intervals during each exposure.
- Air flow rate: Airflow rate through the system was set based on output from the generation equipment and the dilution airflow to provide sufficient volumes for the number of animals to be exposed and for test atmosphere sampling.
- Air change rate: 10 per hour
- Method of particle size determination: Aerosol particle size measurements were conducted during method development as needed and at least twice weekly during the 13-week exposure phase for all test substance exposure groups. Aerosol particle size measurements were conducted using a 7-stage stainless steel cascade impactor. The aerosol size was expressed in terms of the mass median aerodynamic diameter (MMAD) and geometric standard deviation (GSD). The target range for MMAD is 1.0 to 3.0 microns and GSD is 1.5 to 3.5. The mean aerosol particle size exposure system 2, 3 and 4 were 2.1, 1.9 and 1.3 microns, respectively. Mean GSD for exposure system 2, 3 and 4 were 2.35, 2.47 and 2.15, respectively.
- Treatment of exhaust air: exhaust passed through a Solberg canister filter prior to entering the facility exhaust system, which consists of redundant exhaust blowers preceded by activated charcoal- and HEPA-filtration units.
TEST ATMOSPHERE
- Brief description of analytical method used: gravimetric
- Samples taken from breathing zone: yes
VEHICLE (if applicable)
- Justification for use and choice of vehicle: filtered air
- Composition of vehicle: not applicable
- Type and concentration of dispersant aid (if powder): not applicable
- Concentration of test material in vehicle: not applicable
- Lot/batch no. of vehicle (if required): not applicable
- Purity of vehicle: not applicable - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Samples were collected using pre-weighed filters held in a filter holder and placed in the animal breathing zone of an exposure system. A volume of the test atmosphere is pulled through the filter. Following sample collection, the sample is reweighed. The exposure concentration (mg/m3) were calculated by dividing the gravimetrically determined mass of test substance aerosol by the sample volume. The mass was determined by subtracting the initial filter weight from the final weight of the post-sample filter. Sample volume was calculated by multiplying the sample flow rate by the length of the sampling period. Concentrations were not be adjusted for test substance purity. For the test substance exposure systems, samples were collected daily at appropriate intervals based on the target exposure concentrations. For the control group (Group 1), gravimetric samples were collected at least twice weekly during the 13-week exposure period.
- Duration of treatment / exposure:
- 13 weeks
- Frequency of treatment:
- 5 days a week for 6 hours a day
Doses / concentrationsopen allclose all
- Dose / conc.:
- 5 mg/m³ air (nominal)
- Dose / conc.:
- 15 mg/m³ air (nominal)
- Dose / conc.:
- 45 mg/m³ air (nominal)
- Dose / conc.:
- 5.1 mg/m³ air (analytical)
- Dose / conc.:
- 14.9 mg/m³ air (analytical)
- Dose / conc.:
- 44 mg/m³ air (analytical)
- No. of animals per sex per dose:
- 20
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Exposure concentrations were selected to cover a range extending from an anticipated no observed-adverse-effect-concentration (NOAEC) to a concentration in which toxic effects are seen in the highest exposure concentration. Specific concentrations were based on the results of a 28-day range-finding study in which microscopic findings were noted in the lungs, trachea larynx and nasal levels at a concentration of 100 mg/m3.
- Rationale for animal assignment (if not random): random
- Post-exposure recovery period in satellite groups: The animals scheduled for the recovery evaluations will be subjected to necropsy following a 4-week non-exposure period (minimum of 27 days).
Examinations
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: All animals were observed twice daily, once in the morning and once in the afternoon. Moribund animals were euthanized and necropsied as soon as possible. Animals found dead were necropsied as soon as possible to ensure that tissues will not be lost due to autolysis.
- Cage side observations checked in table were included: mortality, abnormalities, and signs of pain and distress
DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Prior to treatment, weekly during the study period and on the day of necropsy
BODY WEIGHT: Yes
- Time schedule: Prior to treatment, twice weekly during the study period and on the day of necropsy
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: Yes / No / Not specified
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule: Once during acclimation prior to randomization and all surviving animals near the end of the exposure period or near the end of the recovery period.
- Dose groups that were examined: all animals
HAEMATOLOGY: Yes
- Time schedule for collection of blood: prior to necropsy
- Anaesthetic used for blood collection: Not specified
- Animals fasted: Yes
- How many animals: all animals
- Parameters checked in table [No.1] were examined.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: prior to necropsy
- Animals fasted: Yes
- How many animals: all animals
- Parameters checked in table [No.1] were examined.
URINALYSIS: Yes
- Time schedule for collection of urine: on the day of necropsy
- Metabolism cages used for collection of urine: Yes
- Animals fasted: Yes
- Parameters checked in table [No.1] were examined.
NEUROBEHAVIOURAL EXAMINATION: No
- Time schedule for examinations: not conducted, as not triggered by clinical observations
IMMUNOLOGY: No - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes (see table No 2)
HISTOPATHOLOGY: Yes (see table No 2) - Statistics:
- All analyses were two-tailed for significance levels of 5% and 1%. All means were presented with standard deviations. All statistical tests were performed by a computer with appropriate programming as referenced below.
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- There were no clinical observations attributable to treatment in the low and mid-dose groups, or in the recovery groups. There were no clinical signs noted 0-1 hour following exposure in any group.
The only group with clinical signs of toxicity due to treatment was the high dose (45 mg/m3) group during the treatment period. Males and females of this group had multiple instances of red, brown, and/or yellow material on various body surfaces and clear discharge around the eyes. The staining was judged by the study author to be indicative of test substance-related stress or general ill health. This finding was observed prior to dosing and on non-exposure days during the treatment period. - Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- One male in the 15 mg/m3 group was euthanized in extremis on Study Day 61 due to a clinical observation of red penile discharge. At necropsy, this male was noted with gross observations of dilated pelvis, distended bladder, distended ureters, and red fluid in the bladder and ureters. This death was not considered to be test substance-related. In addition, a single male in the control group was found dead on Study Day 65; there were no remarkable clinical observations or gross observations noted for this animal. All other animals survived to the scheduled necropsies.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- There were no treatment-related effects on body weight or body weight gain in the low and mid-dose groups.
Test substance-related effects on body weights were noted in the 45 mg/m3 group males and females. Lower mean body weights and cumulative body weight gains were noted beginning as early as Study Week 1 in males and females, which continued until the primary necropsy (Study Week 13); the differences were generally significant compared to the control group. On Study Week 13 (the day of the primary necropsy), mean body weights in the 45 mg/m3 males and females were 9.7% and 6.4% lower, respectively, than the mean control group body weights. In addition, body weight gains in the 45 mg/m3 group males and females were comparable or higher than the control group values during the recovery period; while mean body weights in the males remained lower (not statistically significant) than the control group. Therefore, the animals recovered once exposure stopped, but males were slightly slower to recover than females. - Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- no effects observed
- Behaviour (functional findings):
- no effects observed
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- The only treatment-related effect on organ weights occurred in the high dose group and was limited to the lungs. There were no adverse findings in the low and mid-dose groups.
At the end of the treatment period: Lung weights (absolute and relative to body and brain weights) tended to be higher with exposure concentration across all groups with statistical significance achieved only at 45 mg/m3. For the males, all group mean and individual animal absolute lung weights, as examples, were within historical control reference ranges. In contrast for the 45 mg/m3 group females, mean absolute and both mean relative weights exceeded their historical control reference ranges and, as an example, 6 individual animal absolute lung weights also exceeded the historical control reference range. The most likely microscopic correlations for the higher lung weights were the findings affecting the bronchioles (epithelial hyperplasia, mixed cell infiltrates and luminal debris). Since none of these findings were seen in either sex at exposure concentrations < 45 mg/m3, the 8% to 10% higher lung weights seen in the 15 mg/m3 group males (and lesser magnitudes of change seen at lower exposure concentrations in both sexes), which were reversible, were considered incidental and unrelated to treatment.
At the end of the recovery period: treatment-related and statistically significant higher lung weights (absolute and/or relative to body and brain weights) persisted in both sexes at exposure concentrations of 45 mg/m3. Although mean absolute lung weight was not statistically significant in the 45 mg/m3 group males, the approximately 10% increase was considered sufficient to be considered an effect of test substance exposure. Peribronchiolar chronic inflammation was considered the microscopic correlate for the persistent high lung weights in this group. - Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Macroscopic findings were observed in the high dose group only at the end of the treatment period and were limited to the lungs. There were no adverse findings in any of the groups at the end of the recovery period.
Treatment-related findings of not fully collapsed (3/10 males and 8/10 females) and pale lungs (1/10 males and 2/10 females) were observed exclusively in the 45 mg/m3 group at the primary necropsy; luminal debris in the bronchioles and peribronchiolar inflammatory cell infiltrates appeared to be the microscopic correlates for lungs not fully collapsed while a correlation was not observed for pale lungs. At the Study Week 17 recovery necropsy, not fully collapsed lungs
was seen in 2 males and 1 female from the 45 mg/m3 group but also 1 male each from the control and 5 mg/m3 groups. Therefore at the recovery necropsy, lungs not fully collapsed was not conclusively associated with exposure to the test substance aerosol. - Neuropathological findings:
- no effects observed
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- See Tables 3 to 6.
Treatment-related microscopic findings were limited to the respiratory tract. These findings were observed in all groups at the end of the treatment period, but they were only observed in the high dose group at the end of the recovery period.
At the end of the treatment period: In the nasal cavity treatment-related epithelial (transitional, respiratory, or olfactory) degeneration/regeneration was characterized by loss of normal tissue architecture, most commonly by cell loss and replacement by a single layer of attenuated epithelium; these changes were typically bilateral. Specific to the respiratory epithelium was loss of cilia and reduction/loss of goblet cells. The sites of respiratory epithelial degeneration/regeneration were most commonly the dorsal aspect of the nasal septum and lining the dorsal meatus, including nasal turbinate(s). Olfactory epithelial degeneration/regeneration was limited to 1 female in the 45 mg/m3 group and was diffuse within the dorsal meatus of nasal level III while focal and unilateral in the posterior nasal levels. Transitional epithelial degeneration/regeneration was most commonly limited to the tissues lining the lateral meatus (nasal turbinates and lateral wall). Squamous cell metaplasia and mixed cell inflammation were usually associated with areas of epithelial degeneration/regeneration. Squamous cell metaplasia represented a change from the normal epithelium lining a region to an attenuated stratified and keratinized squamous epithelium. Mixed cell inflammation was characterized by a mononuclear cell (lymphocytes, plasma cells and macrophages) population admixed with variable numbers of neutrophils. In contrast to epithelial degeneration/regeneration seen most commonly in the females, transitional and respiratory epithelial hyperplasia was the most common epithelial change seen in the males exposed to test substance aerosol; affected regions were comparable to those seen with degeneration/regeneration in the females. Several of these findings (transitional epithelial hyperplasia, mixed cell inflammation, and squamous cell metaplasia) at nasal level II were seen in one or both sexes at exposure concentrations of 5, 15, and 45 mg/m3.
In the larynx, trachea, and bronchi (recorded under lungs) treatment-related respiratory epithelial degeneration/regeneration and mixed cell inflammation were comparable to that seen in the nasal cavity. It was not uncommon in control group animals to see respiratory epithelial loss and/or attenuation at these sites. Loss was clearly an artifact of tissue collection/processing while the cause of the thinned epithelium was less certain. However, respiratory epithelial degeneration/regeneration was diagnosed only when there was single cell necrosis, mitotic figure(s) and/or rare neutrophils (sub- or intra-epithelial) associated with the attenuated epithelium. Disruption of the normal epithelial architecture with loss of cilia was also considered degeneration/regeneration. In the larynx, squamous metaplasia was similar to that
seen in the nasal cavity except that it was more commonly seen as a change from the normal non-keratinized stratified epithelium to an attenuated and keratinized stratified squamous epithelium. In addition to mixed cell inflammation in the larynx, chronic active inflammation was also an effect of exposure to the test substance, particularly in the 45 mg/m3 group females, and the epiglottis was a common site of this inflammation. Chronic active inflammation was similar to mixed cell inflammation except in the former, fibroblasts/fibroplasia were present generally indicating inflammation of longer duration. Several of these findings (respiratory epithelial
degeneration of bronchi and mixed cell inflammation of the larynx and bronchi) were seen in one or both sexes at exposure concentrations of 5, 15, and 45 mg/m3.
At the end of the recovery period: In the nasal cavity (levels II and III) most previous effects of exposure persisted in one or both sexes from the 45 mg/m3 group with
incidences and severities that were generally lower than those seen at the primary necropsy. A new effect, and evidence of chronic irritation, was mucous cell hyperplasia of the nasal septum at nasal level II in the males. Due to the low incidence and minimal to mild severity and resolution during the 4-week recovery period, findings in the nasal cavity were considered to be nonadverse at 5 and 15 mg/m3. - Histopathological findings: neoplastic:
- not examined
- Other effects:
- no effects observed
- Details on results:
- In the lungs at the primary necropsy, treatment-related effects were centered on the bronchi and/or bronchioles. Changes in the bronchi were comparable to and considered an extension of the changes seen in the trachea. The most prominent change was noted at the periphery of the lungs at the level of the terminal bronchioles. In control group animals, terminal bronchioles rarely had any associated inflammatory or mononuclear cell infiltrates and the epithelial lining
was an admixture of ciliated respiratory epithelial cells and cells with distinct apical blebbing (club/Clara cells). Exposure-related effects included variably dense perivascular and/or peribronchiolar mixed cell infiltrates characterized by mononuclear cells with generally fewer eosinophils and/or neutrophils and in some cases the suggestion of increased fibrosis/fibroplasia (Masson’s stain suggested this was true in a 45 mg/m3 group female evaluated). There was loss of the normal epithelium lining the terminal bronchioles with replacement by a prominent respiratory epithelium with a robustly ciliated epithelium; club cells were generally absent (mild respiratory epithelial hyperplasia). With minimal respiratory epithelial hyperplasia, club cells were occasionally present and/or there was epithelial alteration comparable to the respiratory epithelial degeneration/regeneration noted in the bronchi. Some animals had bronchiolar luminal debris (exudate) consisting of a mucinous material admixed with foamy alveolar macrophages and less commonly neutrophils. It was this exudate in combination with the peribronchiolar cellular infiltrates and respiratory epithelial hyperplasia that were the most likely microscopic correlations for the lungs noted at necropsy as not fully collapsed. Other than the changes affecting the bronchi, discussed above, all treatment-related effects to the lower airways were limited to the 45 mg/m3 group.
In the lungs at the recovery necropsy, some of the previous effects of exposure persisted in one or both sexes from the 45 mg/m3 group with incidences and severities that were generally lower than those seen at the primary necropsy. A new effect, and evidence of chronic irritation, was the shift from mixed cell peribronchiolar infiltrates to chronic inflammation of the bronchioles. Chronic inflammation was characterized by peribronchiolar fibrosis admixed with mononuclear cell infiltrates. Although the absence of club cells was a component of respiratory epithelial hyperplasia of the bronchioles at Study Week 13, they remained reduced in number to absent at the recovery necropsy. Aggregates of pigmented alveolar macrophages, most likely containing hemosiderin, was also a new apparent effect of test substance administration in the 45 mg/m3 group males. Two males from the 45 mg/m3 group had proliferative changes characterized as ‘atypical’ including bronchiolo-alveolar hyperplasia and bronchial mucous cell metaplasia.
Effect levels
- Key result
- Dose descriptor:
- NOAEC
- Effect level:
- ca. 15 mg/m³ air (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- histopathology: non-neoplastic
- organ weights and organ / body weight ratios
Target system / organ toxicity
- Key result
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 45 mg/m³ air (nominal)
- System:
- other: whole respiratory tract
- Organ:
- larynx
- lungs
- nasal cavity
- trachea
- Treatment related:
- yes
- Dose response relationship:
- yes
- Relevant for humans:
- yes
Any other information on results incl. tables
Table 3 Incidence of Selected Histopathologic Findings, Study Week 13 Primary Necropsy - males
Males |
||||
Exposure Concentration (mg/m3) |
0 |
5 |
15 |
45 |
Nasal level IIa |
11b |
10 |
11b |
10 |
Degeneration/regeneration, respiratory epithelium |
0 |
0 |
0 |
2 |
Minimal |
- |
- |
- |
2 |
Mild |
- |
- |
- |
0 |
Moderate |
- |
- |
- |
0 |
Degeneration/regeneration, transitional epithelium |
0 |
0 |
0 |
0 |
Minimal |
- |
- |
- |
- |
Mild |
- |
- |
- |
- |
Moderate |
- |
- |
- |
- |
Marked |
- |
- |
- |
- |
Hyperplasia, respiratory epithelium |
0 |
0 |
0 |
6 |
Minimal |
- |
- |
- |
4 |
Mild |
- |
- |
- |
2 |
Hyperplasia, transitional epithelium |
1 |
4 |
6b |
3 |
Minimal |
1 |
4 |
6b |
2 |
Mild |
0 |
0 |
0 |
1 |
Inflammation, mixed cell |
0 |
2 |
5 |
10 |
Minimal |
- |
2 |
4 |
10 |
Mild |
- |
0 |
1 |
0 |
Metaplasia, squamous cell |
0 |
1 |
4 |
6 |
Minimal |
- |
1 |
4 |
4 |
Mild |
- |
0 |
0 |
2 |
Nasal level IIIa |
11b |
NA |
NA |
10 |
Degeneration/regeneration, olfactory epithelium (marked) |
0 |
- |
- |
0 |
Degeneration/regeneration, respiratory epithelium |
0 |
- |
- |
1 |
Minimal |
- |
- |
- |
1 |
Mild |
- |
- |
- |
0 |
Larynxa |
11b |
10 |
10b |
10 |
Degeneration/regeneration, respiratory epithelium(minimal) |
0 |
0 |
1 |
4 |
Inflammation, chronic active |
0 |
0 |
2 |
1 |
Minimal |
- |
- |
0 |
0 |
Mild |
- |
- |
2 |
1 |
Inflammation, mixed cell |
2 |
2 |
5b |
6 |
Minimal |
2 |
2 |
3b |
4 |
Mild |
0 |
0 |
2 |
2 |
Metaplasia, squamous cell |
0 |
0 |
0 |
2 |
Minimal |
- |
- |
- |
1 |
Mild |
- |
- |
- |
1 |
Tracheaa |
11b |
9 |
11b |
10 |
Degeneration/regeneration, respiratory epithelium |
0 |
0 |
3b |
7 |
Minimal |
- |
- |
2b |
5 |
Mild |
- |
- |
1 |
2 |
Moderate |
- |
- |
0 |
0 |
Inflammation, mixed cell (minimal) |
1b |
0 |
1 |
3 |
Lungsa |
11b |
10 |
11b |
10 |
Degeneration/regeneration, respiratory epithelium, bronchus |
0 |
4 |
9b |
7 |
Minimal |
- |
4 |
9b |
5 |
Mild |
- |
0 |
0 |
2 |
Hyperplasia, respiratory epithelium, bronchioles |
0 |
0 |
0 |
7 |
Minimal |
- |
- |
- |
6 |
Mild |
- |
- |
- |
1 |
Infiltrate, mixed cell, peribronchiolar |
0 |
0 |
0 |
7 |
Minimal |
- |
- |
- |
3 |
Mild |
- |
- |
- |
4 |
|
|
|
|
|
Inflammation, mixed cell, bronchus |
0 |
3 |
3 |
4 |
Minimal |
- |
3 |
3 |
3 |
Mild |
- |
0 |
0 |
1 |
Luminal debris, bronchioles |
0 |
0 |
0 |
2 |
Minimal |
- |
- |
- |
0 |
Mild |
- |
- |
- |
2 |
a Number of tissues examined from each group.
b Includes 1 FD/EE rat.
BOLDED incidences represent effects of exposure to N-[3-(trimethoxysilyl)propyl]ethylenediamine, CAS 1760-24-3
Table 4 Incidence of Selected Histopathologic Findings, Study Week 13 Primary Necropsy - females
|
Females |
|||
Exposure Concentration (mg/m3) |
0 |
5 |
15 |
45 |
Nasal level IIa |
10 |
10 |
10 |
10 |
Degeneration/regeneration, respiratory epithelium |
0 |
0 |
0 |
8 |
Minimal |
- |
- |
- |
2 |
Mild |
- |
- |
- |
2 |
Moderate |
- |
- |
- |
4 |
Degeneration/regeneration, transitional epithelium |
0 |
0 |
1 |
8 |
Minimal |
- |
- |
1 |
1 |
Mild |
- |
- |
0 |
1 |
Moderate |
- |
- |
0 |
2 |
Marked |
- |
- |
0 |
4 |
Hyperplasia, respiratory epithelium |
0 |
0 |
0 |
0 |
Minimal |
- |
- |
- |
- |
Mild |
- |
- |
- |
- |
Hyperplasia, transitional epithelium |
0 |
0 |
0 |
0 |
Minimal |
- |
- |
- |
- |
Mild |
- |
- |
- |
- |
Inflammation, mixed cell |
2 |
5 |
4 |
8 |
Minimal |
2 |
3 |
4 |
3 |
Mild |
0 |
2 |
0 |
5 |
Metaplasia, squamous cell |
0 |
0 |
1 |
4 |
Minimal |
- |
- |
0 |
4 |
Mild |
- |
- |
1 |
0 |
Nasal level IIIa |
10 |
10 |
10 |
10 |
Degeneration/regeneration, olfactory epithelium (marked) |
0 |
0 |
0 |
1 |
Degeneration/regeneration, respiratory epithelium |
0 |
0 |
0 |
3 |
Minimal |
- |
- |
- |
1 |
Mild |
- |
- |
- |
2 |
Larynxa |
10 |
10 |
10 |
10 |
Degeneration/regeneration, respiratory epithelium(minimal) |
0 |
0 |
1 |
1 |
Inflammation, chronic active |
0 |
0 |
0 |
5 |
Minimal |
- |
- |
- |
2 |
Mild |
- |
- |
- |
3 |
Inflammation, mixed cell |
1 |
4 |
7 |
7 |
Minimal |
1 |
4 |
5 |
6 |
Mild |
0 |
0 |
2 |
1 |
Metaplasia, squamous cell |
0 |
0 |
0 |
5 |
Minimal |
- |
- |
- |
5 |
Mild |
- |
- |
- |
0 |
Tracheaa |
10 |
10 |
10 |
10 |
Degeneration/regeneration, respiratory epithelium |
0 |
0 |
2 |
8 |
Minimal |
- |
- |
1 |
3 |
Mild |
- |
- |
1 |
4 |
Moderate |
- |
- |
0 |
1 |
Inflammation, mixed cell (minimal) |
0 |
0 |
1 |
5 |
Lungsa |
10 |
10 |
10 |
10 |
Degeneration/regeneration, respiratory epithelium, bronchus |
0 |
1 |
5 |
9 |
Minimal |
- |
1 |
5 |
7 |
Mild |
- |
0 |
0 |
2 |
Hyperplasia, respiratory epithelium, bronchioles |
0 |
0 |
0 |
10 |
Minimal |
- |
- |
- |
10 |
Mild |
- |
- |
- |
0 |
Infiltrate, mixed cell, peribronchiolar |
0 |
0 |
0 |
10 |
Minimal |
- |
- |
- |
5 |
Mild |
- |
- |
- |
5 |
|
|
|
|
|
Inflammation, mixed cell, bronchus |
0 |
1 |
0 |
6 |
Minimal |
- |
1 |
- |
6 |
Mild |
- |
0 |
- |
0 |
Luminal debris, bronchioles |
0 |
0 |
0 |
7 |
Minimal |
- |
- |
- |
3 |
Mild |
- |
- |
- |
4 |
a Number of tissues examined from each group.
b Includes 1 FD/EE rat.
BOLDEDincidences represent effects of exposure to N-[3-(trimethoxysilyl)propyl]ethylenediamine, CAS 1760-24-3
Table 5 Incidence of Selected Histopathologic Findings, Study Week 17 Recovery Necropsy - males
|
Males |
|||
Exposure Concentration (mg/m3) |
0 |
5 |
15 |
45 |
Nasal level IIa |
9 |
10 |
9 |
10 |
Degeneration/regeneration, respiratory epithelium(minimal) |
0 |
0 |
0 |
1 |
Degeneration/regeneration, transitional epithelium |
0 |
0 |
0 |
1 |
Minimal |
- |
- |
- |
1 |
Mild |
- |
- |
- |
0 |
Hyperplasia, mucous cell (minimal) |
0 |
1 |
1 |
5 |
Hyperplasia, respiratory epithelium (mild) |
0 |
0 |
0 |
2 |
Inflammation, mixed cell |
2 |
1 |
1 |
3 |
Minimal |
2 |
1 |
1 |
1 |
Mild |
0 |
0 |
0 |
2 |
Nasal level IIIa |
NA |
NA |
NA |
NA |
Degeneration/regeneration, olfactory epithelium (moderate) |
- |
- |
- |
- |
Inflammation, mixed cell (mild) |
- |
- |
- |
- |
Larynxa |
9 |
10 |
9 |
10 |
Degeneration/regeneration, respiratory epithelium(minimal) |
0 |
0 |
0 |
0 |
Inflammation, chronic |
0 |
0 |
0 |
4 |
Minimal |
- |
- |
- |
1 |
Mild |
- |
- |
- |
3 |
Tracheaa |
9 |
10 |
9 |
10 |
Degeneration/regeneration, respiratory epithelium (Minimal) |
0 |
0 |
0 |
0 |
Inflammation, mixed cell (minimal) |
0 |
0 |
0 |
0 |
Lungsa |
9 |
10 |
9 |
10 |
Decreased club cells, terminal bronchioles (Present) |
0 |
0 |
0 |
8 |
Degeneration/regeneration, respiratory epithelium, bronchus (Minimal) |
0 |
0 |
0 |
0 |
Inflammation, chronic, bronchioles (Minimal) |
0 |
0 |
0 |
7 |
Luminal debris, bronchioles (Minimal) |
0 |
0 |
0 |
2 |
Macrophages, pigmented (Minimal) |
0 |
1 |
0 |
3 |
a Number of tissues examined from each group.
BOLDEDincidences represent effects of exposure to N-[3-(trimethoxysilyl)propyl]ethylenediamine,
CAS 1760-24-3
There were no other test substance-related histologic changes. Remaining histologic changes were considered to be incidental findings or related to some aspect of experimental manipulation other than exposure to N-[3-(trimethoxysilyl)propyl]ethylenediamine. There was no test substance-related alteration in the prevalence, severity, or histologic character of those incidental tissue alterations.
Table 6 Incidence of Selected Histopathologic Findings, Study Week 17 Recovery Necropsy - females
|
Females |
|||
Exposure Concentration (mg/m3) |
0 |
5 |
15 |
45 |
Nasal level IIa |
10 |
10 |
10 |
10 |
Degeneration/regeneration, respiratory epithelium(minimal) |
0 |
0 |
0 |
1 |
Degeneration/regeneration, transitional epithelium |
0 |
0 |
0 |
2 |
Minimal |
- |
- |
- |
0 |
Mild |
- |
- |
- |
2 |
Hyperplasia, mucous cell (minimal) |
0 |
0 |
0 |
0 |
Hyperplasia, respiratory epithelium (mild) |
0 |
0 |
0 |
0 |
Inflammation, mixed cell |
2 |
0 |
1 |
5 |
Minimal |
2 |
- |
1 |
4 |
Mild |
0 |
- |
0 |
1 |
Nasal level IIIa |
10 |
10 |
10 |
10 |
Degeneration/regeneration, olfactory epithelium (moderate) |
0 |
0 |
0 |
1 |
Inflammation, mixed cell (mild) |
0 |
0 |
0 |
1 |
Larynxa |
10 |
10 |
10 |
10 |
Degeneration/regeneration, respiratory epithelium(minimal) |
0 |
0 |
0 |
3 |
Inflammation, chronic |
0 |
0 |
0 |
6 |
Minimal |
- |
- |
- |
3 |
Mild |
- |
- |
- |
3 |
Tracheaa |
10 |
10 |
10 |
10 |
Degeneration/regeneration, respiratory epithelium (Minimal) |
0 |
0 |
0 |
1 |
Inflammation, mixed cell (minimal) |
0 |
0 |
0 |
1 |
Lungsa |
10 |
10 |
10 |
10 |
Decreased club cells, terminal bronchioles (Present) |
0 |
0 |
0 |
10 |
Degeneration/regeneration, respiratory epithelium, bronchus (Minimal) |
0 |
0 |
0 |
1 |
Inflammation, chronic, bronchioles (Minimal) |
0 |
0 |
0 |
9 |
Luminal debris, bronchioles (Minimal) |
0 |
0 |
0 |
5 |
Macrophages, pigmented (Minimal) |
0 |
0 |
0 |
0 |
a Number of tissues examined from each group.
BOLDEDincidences represent effects of exposure to N-[3-(trimethoxysilyl)propyl]ethylenediamine,
CAS 1760-24-3
There were no other test substance-related histologic changes. Remaining histologic changes were considered to be incidental findings or related to some aspect of experimental manipulation other than exposure to N-[3-(trimethoxysilyl)propyl]ethylenediamine. There was no test substance-related alteration in the prevalence, severity, or histologic character of those incidental tissue alterations.
Table 7 Correlation of Selected Observations
Necropsy |
Organ Weight |
Clinical Pathology |
Histopathology |
Lung- not fully collapsed (PN; 45 mg/m3) |
↑ lung weight |
- |
Lung - Luminal debris, bronchioles; respiratory epithelial hyperplasia of the bronchioles and mixed cell infiltrate, peribronchiolar |
- |
↑ lung weight (RN; 45 mg/m3) |
- |
Lung- Luminal debris, bronchioles and chronic inflammation, bronchioles |
Relationships were suspected between gross necropsy, organ weight, clinical pathology, and histopathology observations, as presented in Table 7. These proposed relationships were based on subjective interpretation rather than a statistical analysis of correlation.
Applicant's summary and conclusion
- Conclusions:
- In a 90-day repeated dose toxicity study conducted to OECD TG 413 and in compliance with GLP, exposure of Sprague-Dawley rats to N-[3-(trimethoxysilyl)propyl] ethylenediamine via nose-only inhalation for 6 hours per day on a 5-day basis for 13 weeks at target exposure concentrations of 5, 15, and 45 mg/m3 resulted in non-adverse test substance-related effects at 5 and 15 mg/m3. Adverse test substance-related clinical observations, lower body weights and body weight gains, macroscopic findings in the lungs, increased lung weights, and microscopic findings in the nasal cavity, larynx, trachea, and lungs were noted in the 45 mg/m3 group males and females at the end of the treatment period. At the recovery necropsy, many of the effects of test substance exposure, including higher lung weights, persisted in the nasal cavity, larynx, trachea, and lungs in the 45 mg/m3 group and were noted at generally a lower incidence and severity than that seen at the primary necropsy. Therefore, the NOAEC was 15 mg/m3.
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