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Diss Factsheets

Administrative data

Description of key information

Oral; NOEC > 3000 ppm; 90 days rat male/female; equivalent to OECD 408; Reyna (1972)

Key value for chemical safety assessment

Repeated dose toxicity: via oral route - systemic effects

Link to relevant study records
Reference
Endpoint:
sub-chronic toxicity: oral
Type of information:
experimental study
Adequacy of study:
key study
Study period:
Not reported
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: A non-GLP study performed to sound scientific principles with a sufficient level of detail to assess the quality of the submitted data.
Qualifier:
equivalent or similar to guideline
Guideline:
OECD Guideline 408 (Repeated Dose 90-Day Oral Toxicity Study in Rodents)
Deviations:
no
Principles of method if other than guideline:
Male and female Charles River albino rats (15 per sex per treatment group) were dosed with the test material in feed for 90 days at concentrations of 0 (control), 300, 1000 and 3000 ppm. Haematology, clinical chemistry and urinalysis were performed on the control and the high dose group on days 45 and 84. Animals were observed for signs of toxicity daily, and bodyweights were measured weekly. At the end of the 90 day period, all animals were necropsied and assessed for signs of systemic toxicity.
GLP compliance:
no
Limit test:
no
Species:
rat
Strain:
other: Charles River
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Charles River Breeding Laboratories, Inc., North Wilmington, Mass., USA
- Weight at study initiation: 98-99 g males; 115 g females
- Housing: individually
- Diet: standard rat ration (ad libitum)
Route of administration:
oral: feed
Vehicle:
unchanged (no vehicle)
Details on oral exposure:
DIET PREPARATION
- Rate of preparation of diet (frequency): weekly
- Mixing appropriate amounts with (Type of food): diet was prepared by blending the appropriate amount of test material with standard rat ration in a Hobart Mixer

Analytical verification of doses or concentrations:
not specified
Duration of treatment / exposure:
90 days
Frequency of treatment:
Daily
Remarks:
Doses / Concentrations:
0, 300, 1000, 3000 ppm
Basis:
nominal in diet
No. of animals per sex per dose:
15 males and 15 females per dose
Control animals:
yes, plain diet
Observations and examinations performed and frequency:
CAGE SIDE OBSERVATIONS: Yes
- Time schedule: daily
- Cage side observations checked: abnormal reactions and deaths

BODY WEIGHT: Yes
- Time schedule for examinations: study day 1 and weekly thereafter

FOOD CONSUMPTION: Yes
- Food consumption data were collected for five rats of each sex in every group weekly during the study

HAEMATOLOGY: Yes
- Time schedule for collection of blood: on study days 45 and 84
- Animals fasted: Yes
- How many animals: 10 animals per sex from the control and high dose group
- Parameters examined included: haematocrit value, erythrocyte count, haemoglobin concentration, total leukocyte count and differential leukocyte count

CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: on study days 45 and 84
- Animals fasted: Yes
- How many animals: 10 animals per sex from the control and high dose group
- Parameters examined included: blood urea nitrogen concentration, serum alkaline phosphatase activity, serum glutamic-pyruvic transaminase activity and fasted blood glucose concentration

URINALYSIS: Yes
- Time schedule for collection of urine: on study days 45 and 84
- Metabolism cages used for collection of urine: No data
- How many animals: 10 animals per sex from the control and high dose group
- Parameters examined included: glucose concentration, albumin concentration, microscopic elements examination, pH and specific gravity
Sacrifice and pathology:
GROSS PATHOLOGY: Yes
- Weights of the liver, kidneys, spleen, heart and brain of each rat were determined and recorded

HISTOPATHOLOGY: Yes
- The following tissues were stained with Haematoxylin-Eosin and subjected to microscopic examination: oesophagus, stomach (cardia, fundus, pylorus), small intestine (duodenum, jejunum, ileum), cecum, colon, liver, kidneys, spleen, pancreas, urinary bladder, pituitary gland, adrenal gland, testes, seminal vesicle, ovary, bone marrow, thyroid gland, parathyroid gland, salivary gland, prostate gland, heart, aorta, lung, lymph node (cervical, mesenteric), skeletal muscle, peripheral nerve, bone (femur), spinal cord, uterus, trachea, eye, optic nerve and brain (cerebrum, cerebellum and pons).
Statistics:
Statistical analyses were conducted upon the absolute organ weights and their corresponding ratios to the weight of the body and brain. An Analysis of Variance was conducted first and any significant effects disclosed by that treatment were further studied by t-tests.
Clinical signs:
no effects observed
Description (incidence and severity):
six deaths occurred resulting from trauma incurred during blood collection; they were not considered to be treatment-related.
Mortality:
no mortality observed
Description (incidence):
six deaths occurred resulting from trauma incurred during blood collection; they were not considered to be treatment-related.
Body weight and weight changes:
no effects observed
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:
not examined
Haematological findings:
no effects observed
Clinical biochemistry findings:
no effects observed
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):
A single statistically significant difference in liver to bodyweight ratio was noted although it was not considered to be related to treatment with the test material
Gross pathological findings:
no effects observed
Histopathological findings: non-neoplastic:
no effects observed
Histopathological findings: neoplastic:
not examined
Details on results:
CLINICAL SIGNS AND MORTALITY: Six deaths occurred during the study. All of these deaths resulted from trauma incurred during the collection of blood samples. These deaths occurred in the control as well as the test groups and were not attributed to the ingestion of the test material. There were no untoward behavioural reactions among any of the animals during the study

BODY WEIGHT AND WEIGHT GAIN: No significant differences were noted, in body weights and total weight gains, between test and control rats

FOOD CONSUMPTION: Food consumption was comparable between control and treatment rats

HAEMATOLOGY: No remarkable differences were observed between control and treatment rats

CLINICAL CHEMISTRY: No remarkable differences were observed between control and treatment rats

URINALYSIS: No remarkable differences were observed between control and treatment rats

ORGAN WEIGHTS: A significant difference in liver to bodyweight ratio was observed in rats treated at 3000 ppm, however, the difference was considered to be normal for a random population of albino rats. the lack of any consistent dietary or sex related response indicates that none of the intergroup differences were related to the ingestion of the test material

GROSS PATHOLOGY: No outstanding differences were noted between test and control rats upon gross pathological examination

HISTOPATHOLOGY: Lesions were observed in some animals, most frequently in the trachea and lungs, indicating chronic murine pneumonia. These findings were noted in control as well as treated animals and were therefore considered not to be related to treatment with the test material
Dose descriptor:
NOEL
Effect level:
> 3 000 ppm
Based on:
test mat.
Remarks:
in diet
Sex:
male/female
Basis for effect level:
other: No abnormalities observed in any of the parameters tested.
Critical effects observed:
not specified

Table 1: Bodyweight

Dietary level

(ppm)

Sex

Bodyweight (g)

Week:

Total Average Weight Gain

(g/rats)

0

1

2

3

4

5

6

7

8

9

10

11

12

13

Control

M

99

153

200

233

299

342

378

399

430

469

491

501

501

520

421

F

115

151

176

179

215

228

235

252

261

275

263

286

286

295

180

300

M

98

149

201

242

301

339

410

428

450

473

497

519

519

531

433

F

115

146

173

177

207

222

250

257

264

276

279

288

288

296

181

1000

M

98

140

194

225

289

321

386

414

439

466

483

504

504

523

425

F

115

147

175

179

218

223

252

264

276

289

292

303

303

305

190

3000

M

99

145

201

236

305

347

373

407

432

469

484

509

509

531

432

F

115

146

175

177

215

227

245

256

268

283

292

295

295

313

198

 

Table 2: Food consumption

Dietary level

(ppm)

Sex

Food Consumption (g/rat/seven days)

Week:

Total Food Consumption

(g/rat)

0

1

2

3

4

5

6

7

8

9

10

11

12

13

Control

M

163

78

159

171

208

216

234

216

216

229

167

192

189

187

2409

F

107

83

137

137

150

157

156

136

136

146

171

132

128

161

1801

300

M

158

96

143

164

191

194

209

184

184

225

151

198

175

212

2306

F

114

71

127

126

131

139

128

124

124

140

99

162

113

138

1612

1000

M

136

105

168

186

198

205

194

204

204

226

163

205

200

240

2430

F

106

87

132

141

150

143

148

145

145

148

117

130

133

147

1727

3000

M

193

105

175

190

211

206

191

195

195

229

194

200

195

222

2506

F

117

88

133

138

142

137

154

122

122

151

105

133

127

145

1692

 

Table 3: Liver organ weight and ratio data (summary of mean values)

Dietary level

(ppm)

Organ Weight

(g)

Organ/bodyweight ratio

(g/100 g)

Organ/brain weight ratio

(g/g)

Male

Female

Male

Female

Male

Female

Control

17.847

9.722

3.4286

3.2918

8.8455

5.2663

300

17.975

10.121

3.3770

3.4170

9.4797

5.6009

1000

17.392

9.829

3.3231

3.2415

9.3762

5.5207

3000

15.769

10.006

3.0970*

3.2714

8.1530

5.6215

* Statistically significant at the 95 % Confident level

Conclusions:
Following continued treatment with test material in the diet for a period of 90 days, no abnormalities were observed in any of the parameters tested. Under the conditions of the test, the no observed effect concentration for albino (Charles River) rats can therefore be concluded to be in excess of 3000 ppm when dosed in the diet.
Executive summary:

The toxicity of the test material following repeated exposure, over a 90 day period, to rats was investigated following a procedure similar to that outlined in standard guideline OECD 408. During the study, groups of 15 male and 15 female rats were exposed to test material at dietary levels of 300, 1000 and 3000 ppm. Under the conditions of the study, no abnormalities were revealed in bodyweight gain, food consumption, survival or in the hematology, clinical chemistry, urinanalysis and pathology parameters investigated. The no observed effect concentration can therefore be concluded to be in excess of 3000 ppm.

Endpoint conclusion
Endpoint conclusion:
no adverse effect observed
Dose descriptor:
NOAEL
300 mg/kg bw/day
Study duration:
subchronic
Species:
rat
Quality of whole database:
The two available studies pre-date GLP. All followed a methodology equivalent to that outlined in the standardised guideline OECD 408. Since all studies were not conducted to GLP but were performed to sound scientific principles with a sufficient level of detail to assess the quality of the submitted data, all were assigned a reliability score of 2 according to the criteria outlined by Klimisch (1977). The overall quality of the dataset is therefore good.

Repeated dose toxicity: inhalation - systemic effects

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

Endpoint conclusion
Endpoint conclusion:
no study available

Repeated dose toxicity: dermal - local effects

Endpoint conclusion
Endpoint conclusion:
no study available

Additional information

Oral

In the key study, the toxicity of the test material following repeated exposure, over a 90 day period, to rats was investigated following a procedure similar to that outlined in standard guideline OECD 408. During the study, groups of 15 male and 15 female rats were exposed to test material at dietary levels of 300, 1000 and 3000 ppm. Under the conditions of the study, no abnormalities were revealed in bodyweight gain, food consumption, survival or in the hematology, clinical chemistry, urinanalysis and pathology parameters investigated. The no observed effect concentration was therefore concluded to be in excess of 3000 ppm.

 

A supporting study is available in the form of a 90 day repeated dose toxicity study in dogs during which groups of 4 male and 4 female dogs were exposed to test material at dietary levels of 0, 300, 1000 and 3000 ppm. Under the conditions of the study, no abnormalities were revealed in bodyweight gain, food consumption, survival or in the hematology, clinical chemistry, urinanalysis and pathology parameters investigated. The no observed effect concentration can therefore be concluded to be in excess of 3000 ppm.

Inhalation

In accordance with Column 1 of Annex VIII of Regulation (EC) 1907/2006, the short-term repeated dose toxicity study (28 days) required under information point 8.6.1 should be conducted using the most appropriate route of administration. Inhalation exposure of the substance is considered to be minimal during manufacture and use. Furthermore, the repeated-dose toxicity has already been adequately addressed via the oral route.

Dermal

In accordance with Column 1 of Annex VIII of Regulation (EC) 1907/2006, the short-term repeated dose toxicity study (28 days) required under information point 8.6.1 should be conducted using the most appropriate route of administration. Since skin contact during production/use is unlikely and there is little likelihood of absorption through the skin, the dermal route should not be considered the most appropriate route. Furthermore, the repeated-dose toxicity has already been adequately addressed via the oral route.


Justification for selection of repeated dose toxicity via oral route - systemic effects endpoint:
Reyna was selected as the key study since the test material investigated is relevant to the substance under evaluation in the dossier and the study was conducted in an appropriate rodent species. As the more suitable model, the current study was selected as the key study.

Justification for classification or non-classification

In accordance with the criteria for classification as defined in Annex I, Regulation 1272/2008, the test material does not require classification for specific organ toxicity, repeated dose. The effects observed in the main study are not considered to be toxicologically significant and do not indicate any signs of organ dysfunction.