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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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 17 Dec 1985 - 27 Feb 1986
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 988
- Report date:
- 1988
Materials and methods
- Objective of study:
- other: Pharmacokinetic study
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EPA OPP 85-1 (Metabolism and Pharmacokinetics)
- GLP compliance:
- yes
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
- Reference substance name:
- N'-(3,4-dichlorophenyl)-N,N-dimethyl urea
- IUPAC Name:
- N'-(3,4-dichlorophenyl)-N,N-dimethyl urea
- Details on test material:
- - Analytical purity: 99.7 % and 99.9% (non-radioactive compound)
- Lot/batch No.: KRJ 140881 and APF 144 88100 (non-radioactive compound)
- Radiochemical purity (if radiolabelling): > 99%
- Specific activity (if radiolabelling): Batch 1: 2.65 MBq/mg = 71.5 uCi/mg; Batch 2: 192.4 kBq/mg = 5.2 uCi/mg
- Locations of the label (if radiolabelling): uniformly in the benzene ring
- Storage condition of test material: in solid form in a refridgerator
Constituent 1
Constituent 2
- Radiolabelling:
- yes
- Remarks:
- uniform labelling with carbon-14 in the benzene ring
Test animals
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Winkelmann, Borchen, Germany
- Weight at study initiation: approx. 200 g
- Fasting period before study: daily amount of food was halved one day prior to administration
- Housing: animals were housed in conventional Makrolon cages type II, 5 rats per cage
- Individual metabolism cages: yes, after administration of the (last) dose
- Diet: 18 g of "Altromin 1324" daily
- Water: tap ad libitum
- Acclimation period: at least one week
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 19 -24
- Humidity (%): 32 - 62
- Air changes (per hr): 10 - 15 times per hour
- Photoperiod (hrs dark / hrs light): 12 hour photocycle
Administration / exposure
- Route of administration:
- other: by oral or intravenous route
- Vehicle:
- other: 0.5% aqueous tragacanth gel for oral application and 10% Cremophor in phys. saline
- Details on exposure:
- VEHICLE
- Amount of vehicle (if gavage): 10 mL/kg
HOMOGENEITY AND STABILITY OF TEST MATERIAL:
The supended compound was stable for at least 4 hours as tested by means of TLC - Duration and frequency of treatment / exposure:
- singly administration or once daily for 15 days
Doses / concentrations
- Remarks:
- Doses / Concentrations:
5 mg/kg once i.v.
5 mg/kg or 200 mg/kg p.o (once or 15 times)
- No. of animals per sex per dose / concentration:
- 5
- Control animals:
- no
- Details on study design:
- - Dose selection rationale: Doses were chosen in consideration of the specific activity, the tolerance of compound in administration formulations and references of the EPA guideline
- Details on dosing and sampling:
- PHARMACOKINETIC STUDY (Absorption, distribution, excretion)
- Tissues and body fluids sampled: urine, faeces, blood, tissues, , bile
Results and discussion
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- The radioactivity was almost completely absorbed following oral administration of Diuron. (> 95%)
A total of more than 95 % of the recovered radioactivity was thus found in the urine (57.4 %), bile (37.7 %) and in the residual body (0.5 %) in animals
with bile fistulas. The levels of radioactivity in the blood reached a peak 1.7 to 6.8 hours after treatment. - Details on distribution in tissues:
- The peak levels in the plasma ranged between Pmax = 0.29 - 0.58, i.e. 29 - 58 % of the theoretical equidistribution concentration
of P = 1 in the blood. This indicates a medium rate of distribution from the blood into the tissues.
Only low levels of radioactive residues were found in the animals excluding the gastrointestinal tract three days after treatment
(0.5 - 0.8 % of the balanced radioactivity following a single dose, and 1.1 - 2.5 % after multiple doses).
The dose-normalised concentrations in the animal excluding the gastrointestinal tract after a single dose were P = 0.0054 - 0.0067.
The relative concentrations rose by a factor of 3 - 5 after multiple doses. This indicates that the tissues were not saturated by the 15 multiple doses
indicating accumulation to be unlikely.
Levels markedly higher than the average concentrations in the animal body (by a factor of 2 - 11) were measured in the erythrocytes, kidneys, spleen, adrenals and ovaries, as well as in the liver, plasma and lungs. Lower levels (by a factor of 3 - 4) were found in the musculature, brain and renal fat. However, the overall tissue concentration is very low due to the fast excretion of the radioactivity.
- Details on excretion:
- The radioactivity was rapidly eliminated from the animal body. More than 97 % of the balanced radioactivity was eliminated from the body via urine
and faeces within 72 hours after treatment in all the animal groups. With levels of 68 – 87 %, renal excretion predominated, 50 % of the total being
eliminated within eight hours after treatment and 90 % within 12 hours in nearly all cases.
Male rats with bile cannulae eliminated about 38% of the recovered amount in the bile within 48 hours, about 57% in the urine,
and only about 4% in the faeces indicating entero-hepatic circulation.
Only a small amount of radioactivity (0.01 %) could be detected in the expired air within three days after oral administration of a 200 mg/kg bw dose.
Metabolite characterisation studies
- Metabolites identified:
- not measured
Any other information on results incl. tables
Absorption, distribution and elimination were mainly independent from doses and administration.
Table 1: Excretion of total radioactivity and radioactively labelled residues in the body 72 hours after administration to male rats (values in % of adminstered radioactivity, mean)
Biological material |
200 mg/kg p.o. |
5 mg/kg p.o. |
5 mg/kg i.v. |
5 mg/kg p.o. |
5 mg/kg p.o. mult. dose |
200 mg/kg p.o. mult. dose |
200 mg/kg p.o. |
Bile |
|
35.82 |
|
|
|
|
|
[14C] Carbondioxide |
0.01 |
|
|
|
|
|
|
Urine |
71.20 |
54.50 |
89.77 |
76.42 |
81.26 |
86.60 |
65.56 |
Feces |
20.28 |
4.10 |
15.93 |
15.97 |
16.90 |
16.98 |
30.97 |
Body excl. GIT |
0.75 |
0.46 |
0.53 |
0.49 |
2.56 |
1.16 |
0.54 |
GIT |
0.10 |
0.04 |
0.06 |
0.05 |
0.15 |
0.15 |
0.06 |
Recovery (% of the dose) |
92.33 |
94.94 |
106.29 |
92.92 |
100.87 |
104.89 |
97.13 |
GIT - gastrointestinal tract
Table 2: Excretion of total radioactivity and radioactively labelled residues in the body 72 hours after administration to female rats (values in % of adminstered radioactivity, mean)
Biological material |
200 mg/kg p.o. |
5 mg/kg i.v. |
5 mg/kg p.o. |
5 mg/kg p.o. mult. dose |
200 mg/kg p.o. mult. dose |
200 mg/kg p.o. |
[14C] Carbondioxide |
0.01 |
|
|
|
|
|
Urine |
82.35 |
81.78 |
92.40 |
83.98 |
86.14 |
78.63 |
Feces |
17.20 |
13.11 |
13.78 |
14.80 |
17.86 |
21.75 |
Body excl. GIT |
0.80 |
0.55 |
0.54 |
1.23 |
1.68 |
0.67 |
GIT |
0.09 |
0.07 |
0.07 |
0.16 |
0.15 |
0.07 |
Recovery (% of the dose) |
100.44 |
95.51 |
106.79 |
100.18 |
105.84 |
101.12 |
GIT - gastrointestinal tract
Table 3: Biokinetic parameters from a model free blodd curve analysis
Dose |
5 mg/kg i.v. |
5 mg/kg p.o. |
200 mg/kg p.o. |
|||
Sex |
male |
female |
male |
female |
male |
female |
T abs. (h) T 0.5z (h) |
|
|
0.69 |
0.67 |
1.96 |
1.67 |
27.80 |
32.09 |
34.34 |
28.30 |
26.22 |
30.55 |
|
AUC exp. (h) AUC total (h) |
8.62 |
9.88 |
4.06 |
5.19 |
7.62 |
7.41 |
9.56 |
11.12 |
4.69 |
5.91 |
9.35 |
8.94 |
|
P max. (h) T max. (h) |
|
|
0.58 |
0.57 |
0.37 |
0.29 |
|
|
1.88 |
1.70 |
5.60 |
6.80 |
|
Clearance total (mL/min) Clearance renal (mL/min) |
1.61 |
1.51 |
3.26 |
2.58 |
1.64 |
1.58 |
1.70 |
1.36 |
3.15 |
2.93 |
1.27 |
1.83 |
|
Mean Res. Time (h) Vol. steady state (mL/g) |
19.84 |
22.73 |
29.76 |
29.48 |
31.99 |
39.38 |
2.20 |
2.05 |
5.80 |
4.55 |
3.10 |
4.12 |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): no bioaccumulation potential based on study results
- Executive summary:
In this study, conducted in compliance with EPA OPP 85 -1, Diuron uniformly 14C labelled in the phenyl ring was used to investigate the biokinetic behaviour in Wistar rats. After administration of a single oral dose of 5 or 200 mg/kg bw, or a single intravenous dose of 5 mg/kg bw. or fifteen daily oral doses of 5 or 200 mg/kg bw Diuron, no evidence for bioaccumulation was found. Diuron was almost completely absorbed based on excretion results and rapidly excreted, mainly via the urine within 72 hours. Maximum peak plasma levels were reached between 1.7 and 6.8 hours following administration and increased tissue concentrations were limited to the blood or organs which produce or contain blood and to organs with metabolic or excretory function. (Weber and Abbink 1988)
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