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EC number: 206-354-4 | CAS number: 330-54-1
- 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:
- chronic toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Feb 1982 - Feb 1983
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 985
- Report date:
- 1985
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 452 (Chronic Toxicity Studies)
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- Diuron
- EC Number:
- 206-354-4
- EC Name:
- Diuron
- Cas Number:
- 330-54-1
- Molecular formula:
- C9H10Cl2N2O
- IUPAC Name:
- 3-(3,4-dichlorophenyl)-1,1-dimethylurea
- Details on test material:
- - Analytical purity: 98.2 - 98.5 %
- Lot/batch No.: 232114156
- Stability under test conditions: yes
Constituent 1
Test animals
- Species:
- dog
- Strain:
- Beagle
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Winkelmann, Borchen, Germany
- Age at study initiation: 20 - 27 weeks
- Weight at study initiation: 6.2 - 9.9 kg
- Housing: dogs were kept in individual cages, (110 x 115 cm2 or 110 x 150 cm2)
- Diet: "ssniff HH sole diet for dogs, double ground" daily in the morning (week 1 to 5: 300 g, week 6 to 10: 330g, week 11 to 15: 350 g,
week 16 to 26: 380 g, week 27 to 40: 400 g, week 41 to 53: 430 g)
- Water: tap water ad libitum
- Acclimation period: yes
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20 to 22
- Humidity (%): approx. 50
- Photoperiod (hrs dark / hrs light): 12 hour cycle
Administration / exposure
- Route of administration:
- oral: feed
- Vehicle:
- other: Ssniff HH sole diet for dogs
- Details on oral exposure:
- DIET PREPARATION
- The feed substance mixtures were produced in a mixer granulator type MGT.
- Mixing appropriate amounts with (Type of food): Ssniff HH sole diet for dogs - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Regulary analytical checks throughout the study ensured that the feed-substance mixtures actually contained the declared Diuron concentrations.
Before the start of the study it had been established that the test compound was stable for at least ten days in the dry feed and at least 24 hours in
wet feed, and was homogeneously mixed. - Duration of treatment / exposure:
- 12 months
- Frequency of treatment:
- daily
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0, 50, 300, 1800 ppm
Basis:
nominal in diet
- No. of animals per sex per dose:
- 6
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: substance concentrations administered were based on the results of a pilot test to establish dosage
Examinations
- Observations and examinations performed and frequency:
- DETAILED CLINICAL OBSERVATIONS: Yes
- Time schedule: Behaviour and appearance were assessed several times daily
- mortality was checked several times daily
BODY WEIGHT: Yes
- Time schedule for examinations: weekly
FOOD CONSUMPTION: Yes
- daily recorded as well as time of consumption
WATER CONSUMPTION: Yes
OPHTHALMOSCOPIC EXAMINATION: Yes
- Time schedule for examinations: prior to dosing, then at weeks 6, 13, 26, 39 and 52
HAEMATOLOGY: Yes
- Time schedule for collection of blood: prior to dosing, then at weeks 6, 13, 26, 39 and 52
- How many animals: all
- Parameters checked: haematocrit, haemoglobin concentration, erythrocyte count, total and differential leukocyte count, platelet count, MVV, MCH, MCHC, reticulocyte count, Heinz bodies, thromboplastin time and blood sedimentation rate.
CLINICAL CHEMISTRY: Yes
- Time schedule for collection of blood: prior to dosing, then at weeks 6, 13, 26, 39 and 52
- How many animals: all
- Parameters checked: sodium, potassium, chloride, calcium, glucose, urea, creatinine, total protein, ASAT, ALAT, alkaline phosphatise, GLDH,
bilirubin, cholesterol and serum proteins.
URINALYSIS: Yes
- Time schedule for collection of urine: performed on all animals at weeks 6, 13, 26, 39 and 52
- Parameters checked: pH, protein, glucose, occult blood, ketone bodies, bilirubin, specific gravity and sediment. - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
-All organs were inspected grossly.
- Organ weights were determined for brain, heart, testes, adrenals, kidneys, liver, lungs, ovaries, pancreas, prostate, spleen, and thyroids.
HISTOPATHOLOGY: Yes
- Histopathology was performed for all animals on the following organs: adrenals, aorta, bone marrow, bone, brain, epididymes, oesophagus, eye, gall bladder, heart, kidney, liver, lung, lymph nodes, mammary gland, ovary, pancreas, pituitary gland, prostate, skeletal muscle, intestines, spleen, stomach, testis, thymus, thyroid gland, urinary bladder, uterus, parotis, nervi optici, nervi ischiacus. - Other examinations:
- Body temperature and pulse rate were recorded in weeks -2, 6, 13, 26, 39 and 52.
Reflex tests were performed on each animal before start and in weeks 6, 13, 26, 39 and 52, including pupil reaction, corneal, patellar tendon,
stretch, righting and bending reflex. - Statistics:
- Significance between controls and treated groups was analysed by Wilcoxon’s “two-sided test” (non-parametric rank sum).
Results and discussion
Results of examinations
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Food efficiency:
- no effects observed
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- no effects observed
- Haematological findings:
- no effects observed
- Description (incidence and severity):
- See details on result.
- Clinical biochemistry findings:
- effects observed, treatment-related
- Description (incidence and severity):
- See detail on results.
- 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):
- See detail on results.
- Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- See detail on results.
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- See detail on results.
- Histopathological findings: neoplastic:
- no effects observed
- Details on results:
- CLINICAL SIGNS AND MORTALITY
- No relevant adverse effects on behaviour or appearance for dogs of all groups were noted.
- Vomiting was observed in isolated cases and not related to treatment. Nature of faeces was not affected by Diuron-treatment.
- All animals survived the study.
BODY WEIGHT AND WEIGHT GAIN
- Body weight gain in dogs receiving 50 or 300 ppm was comparable to controls. At 1800 ppm a decrease in body weight gain was presenting the latter part of the study and more pronounced in females.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study)
- Dosing at 50 and 300 produced no adverse effects on food consumption.
Some males of the top dose group left feed residues attributable to treatment.
Females in other groups did also not completely consume their diet, which is due to over-feeding, since feed ration was calculated over all animals.
- The mean quantities of Diuron taken up averaged for both sexes together were calculated to be
131.1 (group I), 778.3 (group II), and 4410.7 mg/animal and week (group III). When calculated for males on a weekly basis,
average uptake was 133.5, 794.1 and 4712.8 mg/animal/week for males in groups I, II and III, respectively.
OPHTHALMOSCOPIC EXAMINATION
- No ocular changes were noted in any of the treatment groups.
HAEMATOLOGY
- Thromboplastin times, blood sedimentation rates and differential blood counts were not affected by treatment.
Red blood cells were affected by Diuron as evidenced by reduced haemoglobin and erythrocyte count and increased mean corpuscular cell volumes of the red blood cells. Moreover, high numbers of Heinz bodies in erythrocytes and increasing reticulocytes in dogs dosed at 1800 ppm indicated an anaemic process and compensation reactions
CLINICAL CHEMISTRY
- Liver alterations were indicated by increased alkaline phosphatase in high dose animals. This finding was supported by slightly increased
cholesterol values. In top dose animals increased bilirubin values were observed pointing to a haemolytic icterus.
URINALYSIS
All results were comparable between controls and dosed dogs
ORGAN WEIGHTS
Testes in top dose males and liver and spleen in all animals of the 1800 ppm group were increased.
GROSS PATHOLOGY and HISTOPATHOLOGY: NON-NEOPLASTIC
Some histopathological findings were related to Diuron-treatment:
- Gross pathology showed dark colouration of bile, spleen, kidney, and bone marrow of mainly high dose animals.
- Iron-containing pigment deposits were found in the livers of top dose females in the Kupffer cells.
- Spleens of high and mid dose animals showed a high incidence of iron-containing pigments in the red pulp.
- Proximal tubuli or kidneys at the higher doses exhibited golden-brown crystalloid pigment.
- Reactive fat-deficient bone marrow with an increased iron.-content in animals of the 1800 ppm group was assessed.
OTHER FINDINGS
Examination of reflexes, pulse rates and body temperature did not reveal any treatment-induced alterations.
Effect levels
open allclose all
- Dose descriptor:
- NOAEL
- Effect level:
- 1.8 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: 50 ppm is equivalent to approximately 1.8 mg/kg/d
- Dose descriptor:
- LOAEL
- Effect level:
- 11 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: 300 ppm is equivalent to approximately 11 mg/kg bw/d. Based on haemolytic anaemia, pigmentation of liver, kidneys and spleens and altered organ weights (liver, spleen)
Target system / organ toxicity
- Critical effects observed:
- not specified
Any other information on results incl. tables
Table 1: Results of a 12 -month repeated dose toxicity study in dogs
Parameter |
Control |
50 ppm |
300 ppm |
1800 ppm |
||||
|
Male |
Female |
Male |
Female |
Male |
Female |
Male |
Female |
Observations |
||||||||
Number of animals examined |
6 |
6 |
6 |
6 |
6 |
6 |
6 |
6 |
Mortality |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
Clinical signs |
None (vomiting sporadically in all groups) |
|||||||
Body weight gain |
NA* |
NA |
NA |
NA |
NA |
NA |
¿ |
¿ |
Food consumption |
NA |
NA |
NA |
NA |
NA |
NA |
¿ |
¿ |
Mean compound intake [mg/kg bw/d] |
0 |
0 |
1.8 |
11 |
64 |
|||
Serum protein analysis |
||||||||
Alpha 2 globulin [%] |
NA |
NA |
NA |
NA |
NA |
NA |
¿ |
¿ |
Beta globulin [%] |
NA |
NA |
NA |
NA |
NA |
NA |
¿ |
¿ |
Organ weights |
||||||||
Liver |
NA |
NA |
NA |
NA |
NA |
NA |
¿ |
¿ |
Spleen |
NA |
NA |
NA |
NA |
NA |
NA |
¿ |
¿ |
Testes |
NA |
NA |
NA |
NA |
NA |
NA |
¿ |
-- |
Histopathology [no. of incidence] |
||||||||
Livera) |
0 |
0 |
1 |
1 |
1 |
0 |
5 |
6 |
Spleenb) |
0 |
0 |
0 |
1 |
4 |
5 |
5 |
3 |
Kidneyc) |
0 |
0 |
1 |
0 |
2 |
4 |
5 |
5 |
Bone marrowd) |
0 |
0 |
0 |
0 |
0 |
1 |
5 |
3 |
NA – not affected
a)deposit of iron-containing pigment in Kupffer cells
b)iron-containing pigment in red pulp region
c)golden brown crystalloid pigment in proximal tubuli
d)reactive fat-deficient bone marrow with increased iron-content
Table 2: Results of clinical chemistry (group means of both sexes)
Dose group |
Week |
Alanine aminotransferase [U/L] |
Alkaline phosphatase [U/L] |
Bilirubin [µmol/L] |
Chloesterol [mmol/L] |
0 ppm |
-2 6 13 26 39 52 |
21.11 20.03 24.83 21.12 27.72 23.62 |
259.1 203.8 198.1 176.6 189.6 147.7 |
2.62 3.42 4.07 3.35 3.42 4.66 |
3.084 2.981 3.014 3.279 3.815 3.125 |
50 ppm |
-2 6 13 26 39 52 |
21.76 21.54 23.00 24.85 30.21 25.61 |
249.1 189.7 1889.3 158.1 142.2 121.2 |
2.82 3.18 3.52 2.87 3.17 3.86 |
2.942 2.975 2.909 3.414 3.774 2.911 |
300 ppm |
-2 6 13 26 39 52 |
23.06 20.14 22.98 22.50 26.51 25.23 |
248.7 175.2 174.8 151.0 145.4 126.2 |
2.73 3.72 3.71 2.66 3.20 4.01 |
2.659 3.725 3.461 3.759 3.452 3.202 |
1800 ppm |
-2 6 13 26 39 52 |
23.36 18.40 21.42 24.77 34.54 31.78 |
265.3 282.9** 368.2*** 396.9*** 552.5*** 381.1*** |
3.12 4.82*** 4.74 3.28 5.02*** 5.16 |
2.981 4.348*** 3.681 4.345*** 4.372 3.589 |
* p =0.05 ** p =0.02 *** p =0.01
Table 3: Chronic toxicity of Diuron to dogs, summarized haematology data (group means from both sexes)
Treatment |
Week |
ERY.1) 1012/L |
HB2) g/L
|
HCT3) L/L |
MCV4) fL |
MCH5) pg |
MCHC6) g/L ERY |
THROMB.7) 109/L |
TPT8) sec |
LEUCO.9) 109/L |
RETIC.10) ‰ |
HEINZ. BODIES ‰ |
Control |
- 2 |
6.203 |
139.3 |
0.4393 |
71.7 |
22.86 |
315.3 |
297.5 |
7.45 |
16.01 |
7.1 |
|
6 |
6.379 |
149.2 |
0.4482 |
69.3 |
23.8 |
331.9 |
238.5 |
7.78 |
11.63 |
4.7 |
|
|
13 |
6.374 |
148.4 |
0.4880 |
75.3 |
22.97 |
302.8 |
257.8 |
7.87 |
13.47 |
7.2 |
1.3 |
|
26 |
6.810 |
153.4 |
0.4865 |
71.7 |
22.57 |
318.1 |
264.4 |
7.21 |
13.44 |
4.6 |
0.5 |
|
39 |
6.741 |
158.7 |
0.4859 |
72.3 |
23.37 |
324.8 |
261.2 |
9.07 |
13.74 |
7.7 |
1.4 |
|
52 |
6.777 |
160.3 |
0.4558 |
67.9 |
23.70 |
350.3 |
237.8 |
8.99 |
13.76 |
10.4 |
2.8 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Diuron 50 ppm |
- 2 |
6.083 |
137.8 |
0.4397 |
71.8 |
22.73 |
312.3 |
288.8 |
7.50 |
16.02 |
7.8 |
|
6 |
6.118 |
142.8 |
0.4276 |
69.0 |
23.01 |
331.5 |
240.2 |
7.69 |
12.46 |
4.9 |
|
|
13 |
5.915 |
139.6 |
0.4555 |
75.8 |
23.26 |
306.3 |
265.6 |
7.91 |
13.70 |
5.4 |
1.4 |
|
26 |
6.677 |
148.9 |
0.4795 |
71.8 |
22.34 |
313.1 |
280.3 |
7.45 |
14.12 |
4.9 |
0.9 |
|
39 |
6.572 |
152.2 |
0.4748 |
72.6 |
22.98 |
318.7 |
262.0 |
8.64 |
13.00 |
5.2 |
1.3 |
|
52 |
6.745 |
160.2 |
0.4559 |
68.3 |
23.79 |
350.2 |
229.8 |
9.07 |
13.86 |
6.9 |
2.2 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Diuron 300 ppm |
- 2 |
6.229 |
141.0 |
0.4472 |
71.5 |
22.67 |
314.3 |
297.3 |
7.69 |
14.76 |
6.6 |
|
6 |
5.957* |
139.6 |
0.4254 |
70.3 |
23.12 |
327.1* |
298.3*** |
7.78 |
10.31 |
6.8 |
|
|
13 |
5.863** |
139* |
0.4627 |
77.4** |
23.41 |
299.6 |
315.3*** |
7.87 |
11.99 |
8.0 |
3.7 |
|
26 |
6.477 |
144.9 |
0.4745 |
73.3** |
22.41 |
307.7*** |
312.8** |
7.47 |
13.67 |
6.3 |
1.9 |
|
39 |
6.270 |
150.3 |
0.4636 |
74.2* |
23.72 |
322.0 |
323.8*** |
8.92 |
11.68 |
7.1 |
4.2 |
|
52 |
6.636 |
158.1 |
0.4551 |
69.2 |
23.80 |
345.9* |
268.3 |
9.12 |
12.10 |
10.0 |
4.9 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Diuron 1800 ppm |
- 2 |
6.340 |
147.0 |
0.4608 |
72.5 |
23.22 |
317.3 |
295.6 |
7.64 |
16.08 |
7.0 |
|
6 |
5.490*** |
129.9** |
0.4177 |
74.8*** |
23.32 |
309.9*** |
480.7*** |
7.65 |
13.67 |
40.9*** |
|
|
13 |
5.522*** |
132.5** |
0.4550 |
80.8*** |
23.65 |
289.8*** |
455.7*** |
7.96 |
16.64 |
47.2*** |
204.2*** |
|
26 |
5.765*** |
132.3*** |
0.4417 |
76.5*** |
22.95 |
301.8*** |
419.8*** |
7.54 |
16.49* |
44.3*** |
203.8*** |
|
39 |
5.663*** |
137.8*** |
0.4387** |
77.5*** |
24.09 |
312.2*** |
425.0*** |
9.02 |
16.77 |
37.8*** |
409.2*** |
|
52 |
5.938*** |
142.6*** |
0.4257 |
72.3*** |
24.01 |
333.8*** |
359.4*** |
9.10 |
17.35*** |
38.3*** |
427.4*** |
1)erythrocyte counts 2)hemoglobin 3)hematocrit 4)mean corpuscular volume 5)mean corpuscular hemoglobin content
6)mean corpuscular hemoglobin concentration 7)thrombocyte counts 8)thromboplastin time 9)leucocyte counts
10)reticulocyte counts
* p =0,05 ** p =0,02 *** p =0,01
Applicant's summary and conclusion
- Executive summary:
A reliable 12-month chronic toxicity study in dogs was conducted which was equivalent or similar to OECD 452 giudeline. Beagle dogs received 0, 50, 300 or 1800 ppm of Diuron, mixed into the standard dog diet. All animals survived and no treatment-related clinical signs were observed but effects on red blood cell parameters indicated a hypochromic haemolytic process from 300 ppm onwards.
The NOAEL is set to approx. 1.8 mg/kg/d (50 ppm) for both sexes and the LOAEL is assessed to be approx. 11 mg/kg bw/d (300 ppm), based on haemolytic anaemia, pigmentation of liver, kidneys and spleens and altered organ weights. (Hoffmann and Schilde, 1985)
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