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EC number: 203-812-5 | CAS number: 110-88-3
- 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:
- short-term repeated dose toxicity: inhalation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline with acceptable restrictions, incomplete reporting (e.g. organ weigts)
Data source
Referenceopen allclose all
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 983
- Report date:
- 1983
- Reference Type:
- secondary source
- Title:
- 1,3,5-TRIOXANE, CAS Number 110-88-3, USEPA HPV Challenge Program Submission
- Author:
- Trioxane Manufacturers Consortium Members, BASF Performance Copolymers, LLC (Formerly Ultraform Company) and Ticona
- Year:
- 2 000
- Bibliographic source:
- USEPA HPV Submission
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 412 (Subacute Inhalation Toxicity: 28-Day Study)
- GLP compliance:
- no
- Limit test:
- no
Test material
- Reference substance name:
- 1,3,5-trioxane
- EC Number:
- 203-812-5
- EC Name:
- 1,3,5-trioxane
- Cas Number:
- 110-88-3
- Molecular formula:
- C3H6O3
- IUPAC Name:
- 1,3,5-trioxane
- Details on test material:
- - Name of test material (as cited in study report): C-235
- Physical state: white, crystalline solid
- Analytical purity: approx. 100 %
- Storage condition of test material: under refrigeration
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories
- Age at study initiation: males 41 days, females 58 days
- Mean body weight at test initiation: males 204 g (186-213), females 199 g (187-214)
- Diet (e.g. ad libitum): Purina Rodent Laboratory Chow
- Water (e.g. ad libitum): tap water
- Acclimation period: 13 days
ENVIRONMENTAL CONDITIONS
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- whole body
- Vehicle:
- other: unchanged (no vehicle)
- Remarks on MMAD:
- MMAD / GSD: no data (vapor)
- Details on inhalation exposure:
- GENERATION OF TEST ATMOSPHERE / CHAMBER DESCRIPTION
- Exposure apparatus: stainless steel and glass chambers with a total volume of 1 m3 and an effective volume of 760 liters.
- Air flow rate: The chambers were operated dynamically at an airflow rate of 190 liters per minute. This flow provided one complete air change every 5.3 minutes and a 99% equilibrium time of 24.2 minutes
- Generation of 100 and 1000 ppm trioxane: For generation levels at 100 and 1000 ppm, the material was placed in a 1000 ml three-neck round-bottom flask. The flask used for the low-exposure level was maintained at room temperature, while the flask for the mid-exposure level was kept at 50°C by a temperature regulated water bath. Compressed house-line air was used to sweep the atmosphere enriched with vapour from the flask into the inlet portal of the exposure chamber where it was diluted with room-supplied air.
- Generation of 5000 ppm trioxane: For generation of an exposure level at 5000 ppm test substance, the material was placed in a 4000 ml flask. This flask was also maintained at 50°C using a water bath. Room air was drawn through the bulk of the solid test material, and the resultant airstream with vapour was passed undiluted into the inlet portal of the exposure chamber.
- Determination of the nominal exposure concentration: The generation apparatus and test material were weighed before and after each exposure. The difference in weight represented the total amount of test material delivered into the chamber. This divided by the total volume of air, yielded the nominal exposure concentration.
TEST ATMOSPHERE
- Brief description of analytical method used: gas chromatography
- Samples taken from breathing zone: yes, samples were collected for four times daily at a flow rate of 1 liter/minute for 10, 5 and 2.5 minutes for the 100, 1000 and 5000 ppm chambers, respectively. Duplicate samples, taken to clarify values significantly (more than + 20%) at variance with the target concentration, were drawn when necessary. The presence or absence of particulate was checked once each week using a Royco Portable Particle Monitor. - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- The treated groups were exposed to a cumulative mean analytical concentration of 103, 984 and 4940 ppm of test substance, which were in very good agreement with the respective target concentrations of 100, 1000 and 5000 ppm.
- Duration of treatment / exposure:
- 6 hrs/day, five days/week, for 2 weeks
- Frequency of treatment:
- The animals were subjected to a total of 10 exposures
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
100, 1000 and 5000 ppm
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
103, 984, 4940 ppm
Basis:
analytical conc.
- Remarks:
- Doses / Concentrations:
0.38, 3.62, 18.18 mg/l
Basis:
other: Conversion of analytical concentrations into mg/l according to the "Toxicologist´s Pocket Handbook" (Derelanko MJ, CRC Press, 2000, page 60), and considering a molecular weight for trioxan of 90.08 g/mol.
- No. of animals per sex per dose:
- 5
- Control animals:
- yes, concurrent no treatment
Examinations
- Observations and examinations performed and frequency:
- DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: The animals were examined twice a day for mortalities and clinical symptoms of toxicity; detailed physical examinations were conducted twice a week.
BODY WEIGHT: Yes
- Time schedule for examinations: Body weights were recorded prior test initiation, and thereafter, prior and after the first, the fifth and the tenth exposure.
HAEMATOLOGY: Yes
- Time schedule for collection of blood: at the termination of the exposure period
- Anaesthetic used for blood collection: Yes (ether)
- Animals fasted: Yes
- How many animals: all
- Parameters checked: hemoglobin, hematocrit, erythrocytes, platelets, mean corpuscular volume, mean corpuscular hemoglobin, mean corpuscular hemoglobin concentration, clotting time, total and differential leukocytes, erythrocyte morphology, bone marrow differential (control and high concentration level only).
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood:
- Animals fasted: Yes
- How many animals: all
- Parameters checked: serum glutamic pyruvic transaminase (GPT), blood urea nitrogen, fasting glucose, total protein, albumin, globulin, albumin/globulin ratio. - Sacrifice and pathology:
- GROSS PATHOLOGY:
At study termination, all animals were sacrificed for the purpose of necropsy and were subjected to gross pathology. The external surface, all orifices, the cranial cavity, the carcass, the external surfaces of brain and spinal cord, the thoracic, abdominal and pelvic cavities, the viscera and the cervical tissues were examined.
ORGAN WEIGHTS:
Selected organs (brain, heart, kidneys, liver, ovaries, testes and epididymes, spleen) were weighed and organ/body weight ratios were calculated.
HISTOPATHOLOGY:
From a series of tissues collected and preserved in 10% neutral buffered formalin (except for bone marrow which was preserved in absolute methanol), following tissues were selected from the control and high exposure level animals for further histopathological examination: right kidney, liver, lungs, peribronchial lymph nodes, nasal turbinates, thymus and bone marrow smear. For examination, the tissues samples were sectioned and stained with Hematoxylin and Eosin except for the bone marrow smears, which were stained with Wright´s stain. - Statistics:
- Body weight data, hematology and clinical chemistry parameters, organ weights and organ/body weight ratios were analyzed. Mean values of the treated groups were compared to control at each time interval. Statistically significant differences from control were noticed.
Statistical evaluation of equality of means was made by the appropriate one way analysis of variance technique, followed by a multiple comparison procedure if needed. Bartlett's test was performed to determine if groups had equal variance. If the variances were equal, parametric procedures were used; if not, nonparametric procedures were used. The parametric procedures were the standard one way ANOVA using the F distribution to assess significance. If significant differences among the means were indicated, Dunnett's test was used to determine which means were significantly different from the control. If a non parametric procedure for testing equality of means was needed, the Kruskal-Wallis test was used, and if differences were indicated a summed rank test (Dunn) was used to determine which treatments differed from the control.
A statistical test for trend in the dose levels was also performed. In the parametric case ( i .e . equal variance) standard regression techniques with a tes for trend and lack of fit were used. In the non parametric case Jonckheere's test for monotonic trend was used.
The test for equal variance (Bartlett's) was conducted at the 1%, two-sided risk level. All other statistical tests were conducted at the 5% and 1%, two-sided risk level.
Results and discussion
Results of examinations
- Details on results:
- MORTALITIES AND CLINICAL SYMPTOMS OF TOXICITY:
- All animals survived.
- Treatment-related symptoms seen in all treated groups (both sexes) consisted of increased secretory responses (lacrimation and mucoid nasal discharge). In the high exposure group further symptoms included reduced righting reflex and grip strength as well as persistent pupillary constriction. Approximately 50% of all high-exposure animals exhibited respiratory impairment on day 12.
BODY WEIGHT (see table 1):
- A treatment-related decrease in mean body weights throughout most study period was reported for males and females of the high exposure group. The differences from control ranged from approximately -4% on the day following the first exposure (females) to ca. -13% on the day prior to the last exposure (both sexes).
- In addition, slight reductions in body weights were also noted in the low exposure group (females only) and the mid exposure group (both sexes) on the day prior to the last exposure.
HEMATOLOGICAL PARAMETERS (see table 2):
- Treatment-related changes in hematological parameters were reported for both, males and females of the high exposure group.
- Hemoglobin, hematocrit and erythrocyte counts were statistically significantly increased for both males (+12, +13 and +18%, respectively) and females (+9, +10 and +11%, respectively) compared to control.
- The mean total leukocyte counts were reduced for both males (-55%) and females (-23%) in the high exposure group, with the reduction being statistically significant for the males only.
- The differencial leukocyte count for the high exposure group revealed that the lymphocyte counts were elevated whereas the segmented neutrophils were decreased, relative to control values.
CLINICAL-CHEMICAL PARAMETERS (see table 3):
- Treatment-related changes in clinical chemical parameters were reported for both, males and females of the high exposure group.
- Slight to statistically significant increases in mean serum glutamic pyruvic transaminase, total protein and albumin values, and a decrease in fasting glucose values were reported for these animals when compared to their respective controls.
GROSS PATHOLOGY:
- Gross pathological examination was inconspicuous and revealed no treatment-related changes in the test groups.
ORGAN WEIGHTS:
- The mean terminal body weights of the treated animals were slightly to statistically significantly decreased when compared to controls, in a treatment-related pattern; the differences from control were about -14% for the high exposure males and females.
- Mean absolute and relative spleen weights were decreased for the animals of all treated groups; both sexes were affected in the mid and high exposure groups whereas in the low exposure group, only the males were affected. No histopathological examination of this organ was done.
- Increased mean relative weights for all other weighed organs (brain, heart, kidneys, liver, ovaries, testes and epididymes) were associated with the significantly decreased mean terminal body weights exhibited by the animals. In the animals of both sexes of the low and mid exposure levels, only a decrease in mean absolute and relative spleen weights was observed; all other findings occurred sporadically and were not considered to be related to exposure.
HISTOPATHOLOGY:
- Histopathology revealed that the mucosa of the anterior nasal cavity from the high exposure males and females showed squamous metaplasia with necrosis and desquamation (see table 4). Acute rhinitis with neutrophile exudation into the nasal cavity was a concomitant change.
- Other changes revealed by histopathology were sporadically seen in both, control and high exposure animals and were not treatment-related.
- Bone marrow differential counts revealed no differences among groups which were considered to be treatment-related. No abnormal cells were seen, and all expected normal cell types were present. There were no differences in cellular degeneration, necrosis, or cell type distributions; variations in distribution were within acceptable limits.
Effect levels
open allclose all
- Dose descriptor:
- NOAEC
- Remarks:
- systemic
- Effect level:
- 3.62 mg/L air (analytical)
- Sex:
- male/female
- Basis for effect level:
- other: Effects on hematopoietic system and variations on clinical, biochemical parameters in the highest dose group
- Dose descriptor:
- LOAEC
- Remarks:
- local
- Effect level:
- < 0.38 mg/L air
- Sex:
- male/female
- Basis for effect level:
- other: based on respiratory tract irritation at all tested dose levels.
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Table 1. Body weight data
Weights (g) |
||||||
Males |
Prior test start |
Prior to 1st exposure |
After 1st exposure |
Prior exposure 5 |
After exposure 5 |
Prior exposure 12 |
0 ppm |
162 |
202 |
189 |
224 |
214 |
276 |
103 ppm |
163 |
203 |
190 |
226 |
215 |
278 |
984 ppm |
162 |
202 |
187 |
223 |
212 |
268 |
4940 ppm |
163 |
207 |
189 |
202** |
193** |
239** |
Females |
||||||
0 ppm |
183 |
201 |
191 |
198 |
193 |
228 |
103 ppm |
182 |
197 |
184 |
205 |
195 |
219 |
984 ppm |
183 |
199 |
185 |
203 |
192 |
213 |
4940 ppm |
183 |
199 |
183 |
189 |
179 |
200** |
** = p < 0.01
Table 2. Hematological parameters
Dose (ppm) |
HGB (g/dl) |
HCT (%) |
RBC (106/mm) |
Platelets (105/mm) |
MCV (µ3/cell) |
MCH (pg/cell) |
MCHC (g/dl) |
Clot T (min.) |
WBC (103/mm) |
Males |
|||||||||
0 |
13.6±0.3 |
40±1 |
6.20±0.14 |
15.22±3.75 |
65±1 |
22 |
33.9±0.2 |
1.4±0.5 |
13.9±2.4 |
103 |
14.0±0.4 |
41±1 |
6.28±0.31 |
13.43±0.89 |
66±1 |
22.3 |
33.9±0.3 |
1.6±0.2 |
13.8±2.1 |
984 |
13.9±0.5 |
41±1 |
6.11±0.27 |
14.16±3.73 |
67±2 |
22.7 |
34.1±0.4 |
1.4±0.2 |
13.3±3.4 |
4940 |
15.2±0.8** |
45±3** |
6.93±0.42** |
15.14±2.64 |
64±1 |
22 |
34.2±0.3 |
1.7±0.3 |
6.2±1.2** |
Females |
|||||||||
0 |
14.1±0.7 |
42±2 |
6.45±0.38 |
10.77±1.62 |
65±2 |
21.9 |
33.7±0.6 |
1.6±0.2 |
11.0±1.6 |
103 |
14.5±0.3 |
43±1 |
6.76±0.19 |
13.24±1.29 |
64±3 |
21.5 |
33.3±0.5 |
1.5±0.0 |
11.0±1.0 |
984 |
14.8±0.3 |
44±1 |
6.79±0.33 |
13.26±2.91 |
65±2 |
21.8 |
33.8±0.4 |
1.7±0.3 |
10.8±3.8 |
4940 |
15.40.6** |
46±1** |
7.13±0.17** |
11.46±2.59 |
64±1 |
21.7 |
33.7±0.5 |
1.5±0.4 |
8.5±3.1 |
** p<0.01
Table 3. Clinical chemistry parameters
Dose (ppm) |
SGPT (IU/L) |
BUN (mg/dl) |
Glucose (mg/dl) |
Total protein (g/dl) |
Albumin/ globulin |
Males |
|||||
0 |
29±5 |
22.8±1.3 |
149±16 |
5.4±0.1 |
1.7±0.2 |
103 |
32±3 |
21.9±2.9 |
148±8 |
5.7±0.2 |
1.6±0.1 |
984 |
42±16 |
22.7±2.3 |
151±6 |
5.5±0.3 |
1.7±0.3 |
4940 |
44±6 |
24.0±1.7 |
132±9 |
5.7±0.1 |
1.7±0.3 |
Females |
|||||
0 |
26±3 |
24.7±2.5 |
170±16 |
5.5±0.2 |
1.6±0.2 |
103 |
26±3 |
23.0±2.6 |
153±9 |
5.8±0.2 |
1.5±0.1 |
984 |
34±10 |
24.5±1.9 |
165±20 |
5.8±0.3* |
1.5±0.2 |
4940 |
38±11 |
24.0±1.4 |
135±13* |
5.9±0.2 |
1.6±0.1 |
* p<0.05
Table 4. Upper respiratory tract findings:
Findings in the nasal turbinates |
Concentration levels |
||||
0 ppm |
103 ppm |
984 ppm |
4940 ppm |
||
Acute rhinitis |
0/10 |
3/10 |
6/10 |
7/10 |
|
Mucosa |
Squamous metaplasia |
0/10 |
0/10 |
8/10 |
10/10 |
Erosion |
0/10 |
0/10 |
7/10 |
10/10 |
|
Hyperplasia |
0/10 |
0/10 |
2/10 |
0/10 |
Applicant's summary and conclusion
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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