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EC number: 270-115-0 | CAS number: 68411-30-3
- 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: oral
Administrative data
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 1976
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Reference
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Study period:
- 1976
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The purpose of this study is to determine the sub chronic toxicity of LAS in SLC-ICR mice, focusing on the liver and kidneys. Male and female mice were maintained on either test diets (0 and 0.6%) or drinking water (0, 0.07, 0.2 and 0.6%) for 9 months. Mice in 1.8% dose group of both feeding and drinking water study exhibited severe weight loss so LAS administration was stopped after 2 weeks. Mortality, clinical observations and body weights were recorded during the study. All the surviving animals were humanely euthanized at end of 9 months and gross necropsy, enzyme tests on the liver and kidneys were performed and organs weights were measured. No other parameters (histopathology, clinical chemistry and haematological parameters) were evaluated in the study.
- GLP compliance:
- no
- Remarks:
- predates GLP
- Limit test:
- no
- Species:
- mouse
- Strain:
- other: SLC-ICR mice
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Male and female were obtained from Shizuoka Agricultural Cooperative Association for Laboratory Animals
- Age at study initiation: 4-weeks old
- Weight at study initiation: 24 - 31 g (male mice), 20 - 25 g (female mice)
- Fasting period before study: No
- Housing: 5 animals were housed per cage.
- Diet: CE-2 food (from CLEA Japan); ad libitum
- Water: ad libitum
- Acclimation period: 1 week before the start of treatment
ENVIRONMENTAL CONDITIONS
- Temperature: 25 ± 1°C
- Humidity: 50 - 60%
- Air changes: Not reported
- Photoperiod: 12 hours dark /12 hours light
IN-LIFE DATES: Not reported - Route of administration:
- other: oral: drinking water and feed
- Details on route of administration:
- LAS was administered to animals by mixing 0.6 and 1.8% in CE-2 food (CLEA Japan) and dissolving to 0.07, 0.2, 0.6 and 1.8% in drinking water.
- Vehicle:
- other: Test substance was administered either in diet or drinking water.
- Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- 9 months
- Frequency of treatment:
- Continuous in diet or drinking water (ad libitum)
- Dose / conc.:
- 780 mg/kg bw/day (nominal)
- Remarks:
- in diet (corresponding to 0.6% dose level)
- Dose / conc.:
- 2 340 mg/kg bw/day (nominal)
- Remarks:
- in diet (corresponding to 1.8% dose level) was also included, however due to severe weight loss so LAS administration was stopped after 2 weeks.
- Dose / conc.:
- 133 mg/kg bw/day (nominal)
- Remarks:
- in drinking water (corresponding to 0.07% dose level)
- Dose / conc.:
- 380 mg/kg bw/day (nominal)
- Remarks:
- in drinking water (corresponding to 0.2% dose level)
- Dose / conc.:
- 1 140 mg/kg bw/day (nominal)
- Remarks:
- in drinking water (corresponding to 0.6% dose level)
- Dose / conc.:
- 3 420 mg/kg bw/day (nominal)
- Remarks:
- in drinking water (corresponding to 1.8% dose level) was also included, however due to severe weight loss so LAS administration was stopped after 2 weeks.
- No. of animals per sex per dose:
- Feeding study (mixed in diet): 9 males in 0.6% fed group and 8 males in control group; 8 females in control as well as 0.6% fed group
Drinking water study: 9 animals each in test substance treatment groups and 8 animals in control group - Control animals:
- yes, concurrent vehicle
- yes, plain diet
- Positive control:
- No
- Observations and examinations performed and frequency:
- CLINICAL OBSERVATIONS: Yes
- Time schedule: Weekly
BODY WEIGHT: Yes
- Time schedule for examinations: Weekly
FOOD CONSUMPTION AND COMPOUND INTAKE:
- Food consumption: Yes
- Compound intake: Yes
- Time schedule for examinations: Weekly
FOOD EFFICIENCY: No
WATER CONSUMPTION AND COMPOUND INTAKE: Yes
- Time schedule for examinations: Weekly
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: No
CLINICAL CHEMISTRY: No
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No
IMMUNOLOGY: No
OTHER:
- Liver enzyme tests: Glucose 6-phosphatase (G6Pase), lactase dehydrogenase (LDH), GPT and GOT
- Kidney enzyme tests: G6Pase, LDH, GPT, GOT, ALP, acid phosphatase (ACP), Na, K-ATPase, and malate dehydrogenase (MDH) - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
Gross findings were obtained after euthanizing animals and organs were removed for organ weight measurements.
ORGAN WEIGHTS: Heart, lungs, liver, spleen, kidneys, testes and uterus
HISTOPATHOLOGY: No - Clinical signs:
- no effects observed
- Mortality:
- mortality observed, non-treatment-related
- Description (incidence):
- The number of males in 0.2% dose group (drinking water study) decrease from 9 to 5 animals due to an accident with housing management during the experiment.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Dietary study: There was a significant increase in body weight compared to controls in males of 0.6% dose group.
Drinking water study: There was significant inhibition of weight increase in both males and females of 0.6% dose group consuming LAS water compared to controls, while there was a significant increase in body weight compared to controls in males of 0.07% dose group consuming LAS water. - Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Description (incidence and severity):
- Individual daily food consumption was higher in all treatment groups compared to controls.
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- effects observed, treatment-related
- Description (incidence and severity):
- Dietary study: Water consumption was reduced in females and increased in males of 0.6% dose group (dietary study)
Drinking water study: Water consumption was reduced in males of 0.6% dose group and in females of 0.2% dose group and increased in males of 0.07 and 0.2% dose groups and females of 0.07% dose groups. - Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- 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, treatment-related
- Description (incidence and severity):
- Dietary study: In males of 0.6% dose group, the absolute liver weight was significantly increased, in males of 0.6% dose group (dietary study), the relative liver weight was significantly increased. In females, the relative liver weight was significantly increased in all treatment groups.
Drinking water study: In males of 0.07% dose group, the absolute liver weight was significantly increased, in males of 0.2 and 0.6% dose groups, the relative liver weight was significantly increased, and in 0.07% males the relative liver weight was increased. Relative lung, heart and kidney weights were also increased in male mice consuming 0.07% LAS water. In females, the relative liver weight was significantly increased in all treatment groups. Relative spleen, heart and kidney weights were also increased in female mice consuming 0.6% LAS water. - Gross pathological findings:
- not specified
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- effects observed, treatment-related
- Description (incidence and severity):
- Liver enzyme tests:
Dietary study: Only there was reductions in LDH activity in male mice of 0.6% group
Drinking water study: GOT activity in male mice of 0.6% group consuming LAS water were significant. GOT activity in female mice of 0.2% group was also significantly reduced.
Renal enzyme tests: G6Pase was significantly reduced in males and female mice of 0.6% group consuming LAS water compared to controls, and also reduced in other treatment groups. - Dose descriptor:
- other: no NOAEL can be determined for dietary study
- Remarks:
- Dietary study
- Remarks on result:
- other: Only one dose level for LAS was fed to animals throughout the study.
- Dose descriptor:
- NOAEL
- Remarks:
- Drinking water study
- Effect level:
- 133 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- organ weights and organ / body weight ratios
- other: Liver and kidney enzyme levels
- Remarks on result:
- other: This is based on alteration in liver and kidney weights and enzymes levels at higher tested dose levle. As no other parameters (histopathology, clinical chemistry and hematological parameters) were evaluated in the study.
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 380 mg/kg bw/day (nominal)
- System:
- urinary
- Organ:
- kidney
- Treatment related:
- yes
- Dose response relationship:
- yes
- Relevant for humans:
- yes
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 380 mg/kg bw/day (nominal)
- System:
- hepatobiliary
- Organ:
- liver
- Treatment related:
- yes
- Dose response relationship:
- yes
- Relevant for humans:
- yes
- Conclusions:
- Administration of LAS to SLC-ICR mice by either test diets (0 and 0.6) or drinking water (0, 0.07, 0.2 and 0.6) for 9 months (focusing on the liver and kidneys) revealed an NOAEL of 0.07% (133 mg/kg bw/day in drinking water), based on observed adverse effects on organ weight and liver and kidney enzymes. Repeated administration of LAS impair renal and liver function.
- Executive summary:
The 9 months sub-chronic oral toxicity study of LAS was performed in SLC-ICR mice, focusing on the liver and kidneys.
4 weeks old male and female SLC-ICR mice(obtained from Shizuoka Agricultural Cooperative Association for Laboratory Animals) with body weight range 24 - 31 g (males), 20 - 25 g (females) were used in the study. 5 animals were housed in each cage and maintained under controlled environmental conditions (temperature: Average of25 ± 1°C, humidity:50 - 60%, and 12 hours light /12 hours dark). CE-2 diet (from CLEA Japan) and water were provided ad libitum.
The animals were administered daily with the LAS at following dose levels for 9 months:
Mixed in diet: 0 and 0.6% (equivalent to 0 and 780 mg/kg bw/day); 9 males in 0.6% fed group and 8 males in control group; 8 females in control as well as 0.6% fed group
Dissolved in drinking water: 0, 0.07, 0.2 and 0.6 (equivalent to 0,133, 380 and 1140 mg/kg bw/day); 9 animals each in test substance treatment groups and 8 animals in control group
Mice in 1.8% dose group of both feeding and drinking water study exhibited severe weight loss so LAS administration was stopped after 2 weeks.
Clinical observations, water consumption, food consumption and body weights were recorded weekly. At the end of study, blood was collected for estimation of haematological and clinical chemistry parameters. Gross findings were obtained after euthanizing animals and organs were removed for organ weight measurements. Organ weights for brain, heart, lungs, liver, spleen, kidneys, adrenal gland, testes, uterus, and appendix were recorded. Liver and kidney enzymes were also analysed.
No mortality was observed throughout the study. There was significant inhibition of weight increase in both males and females of 0.6% dose group consuming LAS water compared to controls, while there was a significant increase in body weight compared to controls in males of 0.6% dose group fed with LAS in diet and 0.07% dose group consuming LAS water. Individual daily food consumption was higher in all treatment groups compared to controls. Water consumption was reduced in males of 0.6% dose group (drinking water study) and in females of 0.6% dose group (dietary study) and 0.2% dose group (drinking water study) and increased in males of 0.6% dose group (dietary study), 0.07 and 0.2% dose groups (drinking water study) and female of 0.07% dose groups (drinking water study).
In males of 0.6% dose group (dietary study) and 0.07% dose group (drinking water study), the absolute liver weight was significantly increased, in males of 0.6% dose group (dietary study), 0.2 and 0.6 dose groups (drinking water study), the relative liver weight was significantly increased, and in 0.07% (drinking water) males the relative liver weight was increased. Relative lung, heart and kidney weights were also increased in male mice consuming 0.07% LAS water. In females, the relative liver weight was significantly increased in all treatment groups. Relative spleen, heart and kidney weights were also increased in female mice consuming 0.6% LAS water.
There was reductions in LDH activity in male mice of 0.6% group fed with LAS diet and GOT activity in male mice of 0.6% group consuming LAS water were significant. GOT activity in female mice of 0.2% group (drinking water study) was also significantly reduced. G6Pase was significantly reduced in males and female mice of 0.6% group consuming LAS water compared to controls, and also reduced in other treatment groups.
No NOAEL can be identified for dietary study in mice, as only one dose level for LAS was fed to animals throughout the study.
Administration of LAS to SLC-ICR mice by either test diets (0 and 0.6) or drinking water (0, 0.07, 0.2 and 0.6) for 9 months (focusing on the liver and kidneys) revealed an NOAEL of 0.07% (133 mg/kg bw/day in drinking water), based on observed adverse effects on organ weight and liver and kidney enzymes. Repeated administration of LAS impair renal and liver function.
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 976
Materials and methods
- Principles of method if other than guideline:
- The purpose of this study is to determine the sub chronic toxicity of LAS in Wistar JCL rats, focusing on the liver and kidneys. Male and female rats were maintained on either test diets (0, 0.6 and 1.8%) or drinking water (0, 0.07 and 0.2%) for 9 months. 0.6 and 1.8% rats in drinking water study exhibited severe weight loss so LAS administration was stopped after 2 weeks. Mortality, clinical observations and body weights were recorded during the study. All the surviving animals were humanely euthanized at end of 9 months and gross necropsy, haematological, serum biochemical tests, enzyme tests on the liver and kidneys were performed and organs weights were measured. No histopathology was performed.
- GLP compliance:
- no
- Remarks:
- (pre-dates GLP)
- Limit test:
- no
Test material
- Reference substance name:
- Benzenesulfonic acid, C10-14-alkyl derivs., sodium salts
- EC Number:
- 274-070-8
- EC Name:
- Benzenesulfonic acid, C10-14-alkyl derivs., sodium salts
- Cas Number:
- 69669-44-9
- IUPAC Name:
- sodium 4-dodecylbenzenesulfonate
- Test material form:
- not specified
Constituent 1
Test animals
- Species:
- rat
- Strain:
- other: Wistar JCL
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Male and female rats were obtained from Shizuoka Agricultural Cooperative Association for Laboratory Animals
- Age at study initiation: 4-weeks old
- Weight at study initiation: 100 - 124 g (male rats), 82 - 100 g (female rats)
- Fasting period before study: No
- Housing: 5 animals were housed per cage.
- Diet: CE-2 food (from CLEA Japan); ad libitum
- Water: ad libitum
- Acclimation period: 1 week before the start of treatment
ENVIRONMENTAL CONDITIONS
- Temperature: 25 ± 1°C
- Humidity: 50 - 60%
- Air changes: Not reported
- Photoperiod: 12 hours dark /12 hours light
IN-LIFE DATES: Not reported
Administration / exposure
- Route of administration:
- other: oral: drinking water and feed
- Details on route of administration:
- LAS was administered to animals by mixing 0.6 and 1.8% in CE-2 food (CLEA Japan) and dissolving to 0.07 and 0.2% in drinking water.
- Vehicle:
- other: Test substance was administered either in diet or drinking water
- Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- 9 months
- Frequency of treatment:
- Continuous in diet or drinking water (ad libitum)
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0.6 other: %
- Remarks:
- in diet (corresponding to 300 mg/kg bw/day)
- Dose / conc.:
- 1.8 other: %
- Remarks:
- in diet (corresponding to 900 mg/kg bw/day)
- Dose / conc.:
- 0.07 other: %
- Remarks:
- in drinking water (corresponding to 85 mg/kg bw/day)
- Dose / conc.:
- 0.2 other: %
- Remarks:
- in drinking water (corresponding to 145 mg/kg bw/day)
- No. of animals per sex per dose:
- Feeding study (mixed in diet): 8 animals/sex/dose
Drinking water study: 9 animals/sex/dose - Control animals:
- yes, concurrent vehicle
- yes, plain diet
- Positive control:
- No
Examinations
- Observations and examinations performed and frequency:
- CLINICAL OBSERVATIONS: Yes
- Time schedule: Weekly
BODY WEIGHT: Yes
- Time schedule for examinations: Weekly
FOOD CONSUMPTION AND COMPOUND INTAKE:
- Food consumption: Yes
- Compound intake: Yes
- Time schedule for examinations: Weekly
FOOD EFFICIENCY: No
WATER CONSUMPTION AND COMPOUND INTAKE: Yes
- Time schedule for examinations: Weekly
OPHTHALMOSCOPIC EXAMINATION: No
HAEMATOLOGY: Yes
- Time schedule for collection of blood: After 9 months, blood was collected from each animal after euthanizing.
- Anesthetic used for blood collection: No
- Animals fasted: Not specified
- How many animals: Not specified
- Parameters: White blood cells (WBC), red blood cells (RBC), Haemoglobin (Hgb), Haematocrit (Hct), mean corpuscular volume (MCV) and mean corpuscular haemoglobin concentration (MCHC)
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: After 9 months, blood was collected from each animal after euthanizing.
- Animals fasted: Not specified
- How many animals: Not specified
- Parameters: Glutamate oxaloacetate transaminase (GOT), glutamate pyruvic transaminase (GPT), glucose content, urea nitrogen, total cholesterol, albumin, alkaline phosphatase (ALP) and cholinesterase
URINALYSIS: No
NEUROBEHAVIOURAL EXAMINATION: No
IMMUNOLOGY: No
OTHER:
- Liver enzyme tests: Glucose 6-phosphatase (G6Pase), lactase dehydrogenase (LDH) and G6P-DH activity
- Kidney enzyme tests: G6Pase, LDH, GPT, GOT, ALP, acid phosphatase (ACP), Na, K-ATPase, and malate dehydrogenase (MDH) - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes (However, no details in study report in mentioned)
Gross findings were obtained after euthanizing animals and organs were removed for organ weight measurements.
ORGAN WEIGHTS: Brain, heart, lungs, liver, spleen, kidneys, adrenal gland, testes, ovary, uterus, and appendix
HISTOPATHOLOGY: No
Results and discussion
Results of examinations
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- Both female and male rats consuming LAS-containing water exhibited a slight redness at the tips of their facial fur, and coarse fur all over their bodies.
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- There was significant decrease in body weight gain in males and females of 1.8% dose group fed with diet and in males of 0.2% dose group consuming LAS contained water.
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- effects observed, treatment-related
- Description (incidence and severity):
- Increased water consumption was observed in males of 1.8% dose group fed with diet and 0.2% dose group consuming LAS contained water.
- Ophthalmological findings:
- not examined
- Haematological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- A significant reduction in WBC was observed in 0.6% (diet) male rats compared to controls, and a significant reduction in MCV and MCH was observed in 1.8% (diet) female rats compared to controls.
- Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- Except female rats of 0.07% dose group (drinking water), a significant reduction or a reduction in cholesterol was observed in male and female rats of all dose groups compared to controls. GPT was significantly reduced in 0.6% dose group (diet) females, and reduced in females of other treatment groups. GOT was significantly reduced in 1.8% dose group (diet) males, and reduced in both females and males of other treatment groups. Albumin was significantly reduced in 1.8% (diet) males and reduced in males of 0.2% dose group (drinking water) and females of 1.8% dose group (diet). There was significant increase in ALP levels in male and female rats fed with 1.8% LAS-diet and cholinesterase levels in male rats fed with 1.8% LAS-diet.
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- In males of 1.8% (diet), the absolute liver and testes weight was significantly decreased and the relative testes and liver weight was significantly increased and both absolute and relative spleen weight were also significantly reduced.
In females of 1.8% (diet), absolute and relative liver and caecum weight was significantly increased.
There was also significant decrease in absolute and relative heart weight in females of 0.6% (diet) and 0.07% (drinking water) dose groups. - Gross pathological findings:
- not specified
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- effects observed, treatment-related
- Description (incidence and severity):
- Liver enzyme tests:
Dietary study: G6Pase activity was reduced in 1.8% dose group males and females, G6P-DH activity was reduced in 0.6 and 1.8% dose group males and females, LDH activity was reduced in 0.6, 1.8% dose group. GOT and GPT activities were clearly reduced in males, while in females GPT activity was reduced only in 1.8% dose group and GOT activity was reduced in 1.8% dose group animals.
Drinking water study: LDH activity was reduced in 0.2% dose group males. GOT and GPT activities were clearly reduced in males and GOT activity was increased in 0.07 and 0.2% dose group animals.
Renal enzyme tests:
Dietary study: A significant difference was also observed in G6Pase activity. In females, G6Pase, Na, K-ATPase, and LDH activity were significantly reduced in 1.8% dose group (diet) animals
Drinking water study: In males, Na, K-ATPase activity was significantly reduced in 0.2% dose group. A significant difference was also observed in G6Pase activity.
Effect levels
open allclose all
- Dose descriptor:
- LOAEL
- Effect level:
- 300 mg/kg bw/day (nominal)
- Based on:
- act. ingr.
- Remarks:
- (dietery study)
- Sex:
- male/female
- Basis for effect level:
- body weight and weight gain
- clinical biochemistry
- clinical signs
- haematology
- organ weights and organ / body weight ratios
- water consumption and compound intake
- other: Liver and kidney enzyme levels
- Remarks on result:
- other: Adverse effects were observed at all dose levels
- Dose descriptor:
- NOAEL
- Effect level:
- 85 mg/kg bw/day (nominal)
- Based on:
- act. ingr.
- Remarks:
- (drinking water study)
- Sex:
- male/female
- Basis for effect level:
- clinical biochemistry
- other: Liver and kidney enzyme levels
- Remarks on result:
- other: Based on significant decreases in the activities of glutamate-oxalate transaminase and lactate dehydrogenase in males and significant decrease in renal Na,K-ATPase in males and females at 145 mg/kg bw/day (0.2% drinking water).
Target system / organ toxicity
open allclose all
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 145 mg/kg bw/day (nominal)
- System:
- urinary
- Organ:
- kidney
- Treatment related:
- yes
- Dose response relationship:
- yes
- Relevant for humans:
- yes
- Critical effects observed:
- yes
- Lowest effective dose / conc.:
- 145 mg/kg bw/day (nominal)
- System:
- hepatobiliary
- Organ:
- liver
- Treatment related:
- yes
- Dose response relationship:
- yes
- Relevant for humans:
- yes
Any other information on results incl. tables
Table 1: Body weight gain, food, water and sample consumption of rats on administration of LAS for 9 months (Yoneyama et. al., 1976)
Sex | Groups | No. of rats | Initial body weight (g) | Final Body weight (g) | Body weight gain (%) | Food (g/rat/day) | Water (g/rat/day) | Sample (g/kg BW/day) |
Male | Control | 8 | 113.1± 1.156 | 421.6 ± 8.542 | 372.6 ± 5.889 | 15 | 23 | - |
0.6 F | 8 | 110.6 ± 0.925 | 413.5 ± 7.356 | 373.8 ± 6.380 | 16 | 23 | 0.234 | |
1.8 F | 8 | 109.2 ± 2.218 | 341.1 ± 8.008 | 312.5 ± 6.518** | 14 | 33 | 0.747 | |
0.07 W | 9 | 110.6 ± 1.572 | 411.0 ± 5.255 | 371.9 ± 6.908 | 17 | 29 | 0.051 | |
0.2 W | 9 | 108.3 ± 1.900 | 385.1 ± 5.453 | 356.1 ± 6.346 ** | 15 | 33 | 0.148 | |
Female | Control | 8 | 92.3 ± 1.592 | 212.6 ± 4.508 | 230.5 ± 5.420 | 10 | 18 | - |
0.6 F | 8 | 92.1 ± 1.663 | 216.1 ± 7.705 | 234.3 ± 5.753 | 10 | 17 | 0.287 | |
1.8 F | 8 | 90.6 ± 1.463 | 184.8 ± 4.278 | 204.3 ± 5.791 ** | 9 | 18 | 0.969 | |
0.07 W | 9 | 92.7 ± 1.770 | 206.0 ± 3.555 | 222.4 ± 4.478 | 11 | 20 | 0.082 | |
0.2 W | 9 | 91.6 ± 1.893 | 209.3 ± 5.383 | 228.4 ± 3.857 | 12 | 18 | 0.173 |
Values: mean ± S.E.
*p<0.05
**p<0.01
Table 2: Blood components of rats on administration of LAS for 9 months (Yoneyama et. al., 1976)
Sex | Groups | WBC ( x 103) | RBC ( x 106) | HGB (g) | HCT (%) | MCV (µ3) | MCH (µµg) | MCHC (%) |
Male | Control | 5.5±0.414 | 5.7 ± 0.142 | 10.9 ± 0.195 | 28.0 ± 0.663 | 49.0 ± 0.189 | 19.5 ± 0.247 | 39.5 ± 0.504 |
0.6 F | 4.2 ± 0.221 * | 5.9 ± 0.159 | 11.2 ± 0.291 | 29.2 ± 1.059 | 49.6 ± 0.778 | 19.4 ± 0.436 | 38.9 ± 0.851 | |
1.8 F | 4.9 ± 0.461 | 5.8 ± 0.076 | 10.7 ± 0.118 | 27.8 ± 0.561 | 49.2 ± 0.250 | 19.1 ± 0.268 | 38.5 ± 0.499 | |
0.07 W | 4.7 ± 0.209 | 5.9 ± 0.072 | 11.3 ± 0.094 | 29.1 ± 0.317 | 49.2 ± 0.147 | 19.1 ± 0.210 | 38.6 ± 0.447 | |
0.2 W | 4.9 ± 0.304 | 6.0 ± 0.119 | 11.3 ± 0.141 | 29.3 ± 0.566 | 48.8 ± 0.200 | 19.1 ± 0.238 | 38.7 ± 0.493 | |
Female | Control | 2.6 ± 0.297 | 5.6 ± 0.163 | 11.0 ± 0.243 | 28.8 ± 0.859 | 51.7 ± 0.164 | 20.0 ± 0.364 | 38.4 ± 0.689 |
0.6 F | 2.5 ±0.150 | 5.7 ± 0.265 | 11.2 ± 0.485 | 29.3 ± 1.400 | 51.2 ± 0.313 | 19.8 ± 0.356 | 38.5 ± 0.699 | |
1.8 F | 3.7 ± 0.556 | 5.6 ± 0.294 | 10.5 ± 0.599 | 28.2 ± 1.546 | 50.0 ± 0.378 ** | 18.9 ± 0.193* | 37.5 ± 0.294 | |
0.07 W | 2.4 ± 0.213 | 6.0 ± 0.302 | 11.5 ± 0.556 | 30.5 ± 1.551 | 51.5 ± 0.176 | 19.5 ± 0.159 | 37.7 ± 0.299 | |
0.2 W | 2.7 ± 0.328 | 5.6 ± 0.100 | 11.0 ± 0.176 | 28.9 ± 0.624 | 52.0 ± 0.463 | 20.0 ± 0.349 | 38.3 ± 0.601 |
Values: mean ± S.E.
*p<0.05
**p<0.01
Table 3: Biochemical values in serum of rats on administration of LAS for 9 months (Yoneyama et. al., 1976)
Sex | Groups | GOT (K.U/mL) | GPT (K.U/mL) | GLU (mg/dL) | UN (mg/dL) | CHO (mg/dL) | ALB (g/dL) | ALP ((KA-U/dL) | ChE (ΔpH) |
Male | Control | 151.3 ± 7.285 | 107.5 ± 8.177 | 163.0 ± 11.488 | 21.0 ± 0.333 | 77.5 ± 3.417 | 4.87 ± 0.055 | 41.3 ± 1.308 | 0.166 ± 0.010 |
0.6 F | 133.2 ± 5.573 | 102.3 ± 8.485 | 132.2 ± 4.139* | 21.0 ± 0.684 | 71.6 ± 2.314 | 47.2 ± 0.075 | 44.7 ± 2.782 | 0.187 ± 0.013 | |
1.8 F | 126.7 ± 6.439* | 93.0 ± 3.665 | 144.7 ± 10.099 | 23.1 ± 0.490** | 53.0 ± 1.282** | 44.7 ± 0.068** | 82.3 ± 3.731** | 0.281 ± 0.007 ** | |
0.07 W | 142.8 ± 10.111 | 108.5 ± 12.381 | 131.6 ± 3.088* | 22.8 ± 0.647* | 68.2 ± 2.527* | 47.5 ± 0.059 | 44.0 ± 1.239 | 0.131 ± 0.015 | |
0.2 W | 143.8 ± 9.041 | 103.3 ± 9.513 | 165.1 ± 14.043 | 21.0 ± 1.462 | 62.5 ± 2.534** | 43.2 ± 0.251 | 34.4 ± 3.193 | 0.171 ± 0.008 | |
Female | Control | 142.3 ± 14.359 | 104.2 ± 12.474 | 135.5 ± 5.246 | 23.2 ± 0.793 | 95.8 ± 4.778 | 47.1 ± 0.265 | 45.0 ± 5.728 | 0.963 ± 0.073 |
0.6 F | 116.1 ± 5.244 | 68.7 ± 2.670* | 126.4 ± 3.657 | 21.5 ± 0.602 | 86.7 ± 4.230 | 4.85 ± 0.095 | 40.7 ± 1.539 | 1.056 ± 0.023 | |
1.8 F | 133.6 ± 4.007 | 88.1 ± 4.362 | 130.8 ± 3.945 | 26.7 ± 1.935 | 67.8 ± 7.472** | 42.8 ± 0.097 | 73.8 ± 11.808* | 0.861 ± 0.053 | |
0.07 W | 121.2 ± 7.003 | 74.2 ± 13.529 | 127.2 ± 2.035 | 21.9 ± 0.872 | 95.0 ± 3.755 | 49.0 ± 0.187 | 45.6 ± 12.960 | 0.881 ± 0.171 | |
0.2 W | 128.5 ± 12.209 | 85.7 ± 9.362 | 136.1 ± 10.070 | 21.7 ± 0.950 | 77.2 ± 8.826 | 46.8 ± 0.155 | 44.0 ± 5.756 | 1.053 ± 0.042 |
Values: mean ± S.E.
*p<0.05
**p<0.01
Table 4: Organ weight of male and female rats on administration of LAS for 9 months (Yoneyama et. al., 1976)
Sex | Groups | Brain | Heart | Lung | Liver | Spleen | Kidney (R) | Kidney (L) | Adrenal (R) | Adrenal (L) | Testis(R) | Testis(L) | Ovary (R) | Ovary (L) | Caecum | Uterus | |||||||||||||||
g | g/100g | g | g/100g | g | g/100g | g | g/100g | g | g/100g | g | g/100g | g | g/100g | g | g/100g | g | g/100g | g | g/100g | g | g/100g | g | g/100g | g | g/100g | g | g/100g | g | g/100g | ||
Male | Control | 1.987 ± 0.011 | 0.463 ± 0.008 | 1.026 ± 0.018 | 0.239 ± 0.005 | 1.263 ± 0.033 | 0.294 ± 0.008 | 12.7 ± 0.341 | 2.9 ± 0.039 | 0.698 ± 0.014 | 0.162 ± 0.003 | 1.162 ± 0.40 | 0.270 ± 0.008 | 1.184 ± 0.041 | 0.275 ± 0.007 | 18.3 ± 1.117 | 4.2 ± 0.217 | 18.1 ± 0.934 | 4.2 ± 0.225 | 1.591 ± 0.023 | 0.370 ± 0.006 | 1.643 ± 0.027 | 0.382 ± 0.005 | - | - | - | - | 1.238 ± 0.068 | 0.281 ± 0.015 | - | - |
0.6 F | 1.982 ± 0.011 | 0.473 ± 0.007 | 0.971 ± 0.022* | 0.231 ± 0.004 | 1.269 ± 0.042 | 0.302 ± 0.005 | 12.9 ± 0.310 | 3.0 ± 0.049 | 0.682 ± 0.019 | 0.162 ± 0.002 | 1.210 ± 0.026 | 0.290 ± 0.006 | 1.214 ± 0.032 | 0.289 ± 0.007 | 19.6 ± 1.900 | 4.7 ± 0.435 | 17.6 ± 1.602 | 4.2 ± 0.416 | 1.563 ± 0.019 | 0.373 ± 0.004 | 1.585 ± 0.027 | 0.378 ± 0.007 | - | - | - | - | 1.303 ± 0.057 | 0.305 ± 0.010 | - | - | |
1.8 F | 1.827 ± 0.131 | 0.521 ± 0.037 | 0.825 ± 0.026* | 0.235 ± 0.003 | 1.040 ± 0.025** | 0.295 ± 0.002 | 11.5 ± 0.352* | 3.2 ± 0.043** | 0.501 ± 0.163** | 0.143 ± 0.003** | 0.977 ± 0.022** | 0.279 ± 0.007 | 0.982 ± 0.017** | 0.281 ± 0.007 | 17.5 ± 1.370 | 5.0 ± 0.481 | 17.0 ± 0.654 | 4.8 ± 0.146 | 1.455 ± 0.027** | 0.415 ± 0.004** | 1.491 ± 0.033** | 0.425 ± 0.004** | - | - | - | - | 2.205 ± 0.141 ** | 0.647 ± 0.032** | - | - | |
0.07 W | 1.995 ± 0.016 | 0.471 ± 0.006 | 0.981 ± 0.031 | 0.232 ± 0.008 | 1.287 ± 0.021 | 0.304 ± 0.007 | 13.2 ± 0.258 | 3.0 ± 0.052 | 0.682 ± 0.009 | 0.161 ± 0.002 | 1.221 ± 0.018 | 0.288 ± 0.005 | 1.254 ± 0.012 | 0.296 ± 0.005* | 18.6 ± 0.680 | 4.4 ± 0.156 | 19.2 ± 1.024 | 4.5 ± 0.262 | 1.606 ± 0.022 | 0.379 ± 0.006 | 1.566 ± 0.056 | 0.370 ± 0.015 | - | - | - | - | 1.338 ± 0.040 | 0.314 ± 0.009 | - | - | |
0.2 W | 1.881 ± 0.108 | 0.478 ± 0.028 | 0.975 ± 0.183 | 0.247 ± 0.003 | 1.154 ± 0.037* | 0.293 ± 0.007 | 11.6 ± 0.184 | 2.9 ± 0.042 | 0.595 ± 0.013** | 0.150 ± 0.002 | 1.124 ± 0.025 | 0.286 ± 0.007 | 1.154 ± 0.031 | 0.293 ± 0.008 | 18.4 ± 0.914 | 4.6 ± 0.232 | 17.5 ± 1.309 | 4.4 ± 0.354 | 1.483 ± 0.059 | 0.377 ± 0.016 | 1.589 ± 0.013 | 0.404 ± 0.005 | - | - | - | - | 1.210 ± 0.035 | 0.309 ± 0.008 | - | - | |
Female | Control | 1.853 ± 0.023 | 0.846 ± 0.016 | 0.647 ± 0.013 | 0.294 ± 0.003 | 0.870 ± 0.026 | 0.397 ± 0.012 | 6.2 ± 0.150 | 2.8 ± 0.051 | 0.441 ± 0.016 | 0.201 ± 0.006 | 0.650 ± 0.021 | 0.296 ± 0.006 | 0.650 ± 0.021 | 0.296 ± 0.008 | 24.8 ± 1.381 | 11.2 ± 0.443 | 25.7 ± 1.385 | 11.7 ± 0.487 | - | - | - | - | 29.3 ± 2.738 | 13.4 ± 1.226 | 31.2 ± 4.007 | 14.2 ± 1.857 | 0.828 ± 0.010 | 0.377 ± 0.005 | 0.687 ± 0.037 | 0.313 ± 0.017 |
0.6 F | 1.859 ± 0.011 | 0.845 ± 0.027 | 0.595 ± 0.019* | 0.269 ± 0.006** | 0.810 ± 0.032 | 0.367 ± 0.015 | 6.6 ± 0.355 | 2.9 ± 0.061 | 0.425 ± 0.010 | 0.193 ± 0.009 | 0.648 ± 0.023 | 0.292 ± 0.004 | 0.655 ± 0.026 | 0.296 ± 0.008 | 25.8 ± 1.563 | 11.7 ± 0.820 | 24.8 ± 1.641 | 11.3 ± 0.863 | - | - | - | - | 23.3 ± 3.504 | 10.8 ± 1.740 | 32.8 ± 3.120 | 14.9 ± 1.380 | 0.859 ± 0.064 | 0.381 ± 0.015 | 0.660 ± 0.033 | 0.301 ± 0.020 | |
1.8 F | 1.788 ± 0.031 | 0.954 ± 0.015** | 0.455 ± 0.008 | 0.242 ± 0.002 | 0.761 ± 0.028 | 0.405 ± 0.009 | 7.1 ± 0.195** | 3.8 ± 0.082** | 0.351 ± 0.012 ** | 0.187 ± 0.004 | 0.580 ± 0.015 | 0.309 ± 0.003 | 0.586 ± 0.021* | 0.312 ± 0.007 | 19.6 ± 1.981* | 10.3 ± 0.924 | 21.3 ± 1.487* | 11.3 ± 0.609 | - | - | - | - | 25.3 ± 2.853 | 13.4 ± 1.417 | 31.5 ± 2.322 | 16.7 ± 1.165 | 1.436 ± 0.080** | 0.775 ± 0.039** | 0.588 ± 0.066 | 0.312 ± 0.034 | |
0.07 W | 1.854 ± 0.019 | 0.844 ± 0.016 | 0.611 ± 0.011* | 0.277 ± 0.004** | 0.801 ± 0.027 | 0.365 ± 0.014 | 6.3 ± 0.139 | 2.8 ± 0.063 | 0.424 ± 0.007 | 0.193 ± 0.004 | 0.669 ± 0.017 | 0.304 ± 0.006 | 0.677 ± 0.010 | 0.308 ± 0.005 | 22.0 ± 1.619 | 10.0 ± 0.720 | 21.0 ± 1.763 | 9.8 ± 0.790 | - | - | - | - | 30.0 ± 1.490 | 13.6 ± 0.780 | 31.7 ± 2.300 | 12.2 ± 1.200 | 0.785 ± 0.051 | 0.358 ± 0.024 | 0.729 ± 0.051 | 0.331 ± 0.022 | |
0.2 W | 1.691 ± 0.112 | 0.810 ± 0.053 | 0.593 ± 0.015 | 0.287 ± 0.004 | 0.817 ± 0.040 | 0.393 ± 0.021 | 6.1 ± 0.220 | 2.9 ± 0.071 | 0.428 ± 0.014 | 0.205 ± 0.006 | 0.651 ± 0.015 | 0.312 ± 0.006 | 0.670 ± 0.020 | 0.321 ± 0.008* | 23.2 ± 1.495 | 11.1 ± 0.677 | 24.3 ± 1.154 | 11.6 ± 0.431 | - | - | - | - | 28.4 ± 1.633 | 13.6 ± 0.821 | 28.6 ± 1.900 | 13.7 ± 0.830 | 0.800 ± 0.045 | 0.379 ± 0.026 | 0.644 ± 0.032 | 0.308 ± 0.014 |
Values: mean ± S.E.
*p<0.05
**p<0.01
Table 5: Liver enzyme activities of rats on administration of LAS for 9 months (Yoneyama et. al., 1976)
Sex | Groups | G6 Pase (µmoles Pi/mg protein /hr | G6P-DH (x 10-3)ΔE/mg protein / min | LDH ΔE/mg protein / min | GPT (x 102) KU/mg protein | GOT (x 102) KU/mg protein |
Male |
Control | 3.77 ± 0.22 | 60.3 ± 9.9 | 11.33 ± 0.53 | 4.06 ± 0.345 | 5.80 ± 0.525 |
0.6 F | 3.82 ± 0.50 | 40.9 ± 9.1 ** | 10.28 ± 0.84* | 3.94 ± 0.484 | 5.49 ± 0.810 | |
1.8 F | 2.60 ± 0.015** | 36.0 ± 7.7** | 9.26 ± 0.99** | 3.09 ± 0.225** | 4.95 ± 0.510** | |
0.07 W | 3.57 ± 0.36 | 68.0 ± 15.1 | 10.92 ± 0.91 | 3.89 ± 0.360 | 5.61 ± 0.410 | |
0.2 W | 3.71 ± 0.35 | 56.8 ± 14.9 | 9.28 ± 0.71** | 4.10 ± 0.420 | 6.16 ± 0.545 | |
Female | Control | 2.73 ± 0.57 | 143.6 ± 30.0 | 70.6 ± 11.6 | 2.71 ± 0.405 | 4.91 ± 0.635 |
0.6 F | 2.67 ± 0.51 | 100.7 ± 39.9* | 63.4 ± 14.2 | 2.60 ± 0.505 | 4.30 ± 0.560 | |
1.8 F | 2.17 ± 0.15* | 58.5 ± 12.2* | 62.2 ± 4.7 | 2.37 ± 0.225 | 4.05 ± 0.450 ** | |
0.07 W | 2.61 ± 0.20 | 138.3 ± 41.0 | 65.8 ± 8.5 | 2.57 ± 2.290 | 5.61 ± 0.410* | |
0.2 W | 2.76 ± 0.28 | 120.9 ± 27.6 | 66.5 ± 11.3 | 2.89 ± 0.195 | 6.16 ± 0.545** |
Values: mean ± S.D.
*p<0.05
**p<0.01
Table 6: Kidney enzyme activities of rats on administration of LAS for 9 months (Yoneyama et. al., 1976)
Sex | Groups | ALP (µmoles/mg/hr) | ACP (µmoles/mg/hr) | G6Pase (µmoles/mg/hr) | Na, K-A Tpase (µmoles/mg/hr) | GPT (KU/mL) | GOT (KU/mL) | LDH (ΔE/mg/min) | MDH (ΔE/mg/min) |
Male | Control | 16.37 ± 1.984 | 1.80 ± 0.188 | 3.97 ± 0.590 | 3.94 ± 0.613 | 23.99 ± 5.300 | 192.11 ± 35.741 | 0.339 ± 0.043 | 2.308 ± 0.0447 |
0.6 F | 14.44 ± 2.046 | 1.72 ± 0.141 | 3.92 ± 0.618 | 3.63 ± 0.640 | 23.16 ± 5.885 | 199.95 ± 22.869 | 0.334 ± 0.050 | 2.325 ± 0.575 | |
1.8 F | 15.74 ± 1.933 | 1.78 ± 0.179 | 3.47 ± 0.732 | 3.32 ± 1.311 | 21.11 ± 4.690 | 194.18 ± 13.668 | 0.358 ± 0.070 | 2.354 ± 0.554 | |
0.07 W | 14.73 ± 2.387 | 1.85 ± 0.194 | 4.26 ± 0.547 | 3.52 ± 1.170 | 23.85 ± 4.640 | 207.39 ± 21.308 | 0.347 ± 0.098 | 2.617 ± 0.628 | |
0.2 W | 15.03 ± 1.169 | 1.66 ± 0.109 | 4.03 ± 0.428 | 3.09 ± 0.224* | 24.44 ± 3.535 | 202.94 ± 15.708 | 0.362 ± 0.058 | 2.679 ± 0.740 | |
Female | Control | 15.94 ± 3.369 | 2.02 ± 0.182 | 3.96 ± 0.545 | 4.29 ± 1.027 | 28.27 ± 4.407 | 188.33 ± 21.189 | 0.350 ± 0.035 | 2.387 ± 0.601 |
0.6 F | 17.11 ± 2.919 | 2.03 ± 0.179 | 3.63 ± 0.521 | 4.29 ± 0.656 | 30.26 ± 5.736 | 196.48 ± 21.273 | 0.338 ± 0.044 | 2.231 ± 0.433 | |
1.8 F | 16.86 ± 2.369 | 1.85 ± 0.195 | 3.13 ± 0.426** | 3.19 ± 0.613* | 32.60 ± 3.737 | 184.89 ± 11.276 | 0.291 ± 0.025** | 2.181 ± 0.404 | |
0.07 W | 16.24 ± 2.381 | 1.98 ± 0.218 | 3.72 ± 0.443 | 4.14 ± 1.452 | 27.19 ± 3.319 | 198.09 ± 29.803 | 0.322 ± 0.035 | 2.052 ± 0.306 | |
0.2 W | 15.02 ± 3.244 | 1.90 ± 0.136 | 3.45 ± 0.651 | 4.59 ± 1.154 | 27.03 ± 4.430 | 187.36 ± 20.235 | 0.316 ± 0.052 | 2.070 ± 0.362 |
Values: mean ± S.D.
*p<0.05
**p<0.01
Applicant's summary and conclusion
- Conclusions:
- Administration of LAS to Wistar JCL rats by test diets at dose levels of 0, 0.6 and 1.8% for 9 months (focusing on the liver and kidneys) revealed an LOAEL of 0.6% (300 mg/kg bw/day in diet), based on adverse effects at all dose levels.
Administration of LAS to Wistar JCL rats in drinking water at dose levels of 0, 0.07 and 0.2% for 9 months (focusing on the liver and kidneys) revealed an NOAEL of 0.07% (85 mg/kg bw/day in drinking water), based on adverse effects at all dose levels, based on significant decreases in the activities of glutamate-oxalate transaminase and lactate dehydrogenase in males and significant decrease in renal Na,K-ATPase in males and females at 145 mg/kg bw/day (0.2% drinking water). - Executive summary:
A sub-chronic (9 months) repeated dose toxicity study was conducted with C10-14 LAS, sodium salt in male and female Wistar JCL rats. The test substance was administered at the following dose levels: through diet at 0, 0.6 and 1.8% (equivalent to 0, 300 and 900 mg/kg bw/day) to 8 animals/sex/dose and via drinking water at 0, 0.07 and 0.2% (equivalent to 0, 85 and 145 mg/kg bw/day to 9 animals/sex/dose. Rats at the 0.6 and 1.8% dose group exhibited severe weight loss so LAS administration via diet was stopped after 2 weeks. Clinical observations, water consumption, food consumption and body weights were recorded weekly. Terminal blood collection was done for estimation of haematological and clinical chemistry parameters. Gross findings were observed after euthanizing animals and organs were removed for organ weight measurements. No histopathology was performed. Body weight gain was reduced at the highest dose group only. Significant decreases in transaminase activity and renal Na,K-ATPase were seen at 145 mg/kg bw/day. No significant haematological or organ weight changes were noted. Based on significant decrease in the liver and renal enzyme levels at 145 mg/kg bw/day, the systemic toxicity NOAEL was established at 85 mg/kg bw/day (Yoneyama, 1976).
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