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EC number: 203-674-6 | CAS number: 109-46-6
- 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
Endpoint summary
Administrative data
Key value for chemical safety assessment
Effects on fertility
Description of key information
No data on fertility is available on 1,3 -dibutylthiourea.
Effect on fertility: via oral route
- Endpoint conclusion:
- no study available
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Effects on developmental toxicity
Description of key information
In a developmental study in rat, DBTU was foetotoxic in the absence of distinctive maternal effects. However no teratogenic effects related to administration of DBTU were observed at dose levels up to 200 mg/kg/day, a level which was toxic to the dams.
Link to relevant study records
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- not specified
- GLP compliance:
- not specified
- Species:
- rat
- Strain:
- Sprague-Dawley
- Details on test animals or test system and environmental conditions:
- - Source: IFFA CREDO Breeding Laboratories (Saint-Germain-sur-L'Arbresle, France)
- Age: no data
- Weight at study initiation: Males: around 350 g ; Females: 200-220 g - Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on exposure:
- - Total volume applied: 5 ml/kg body wt
- Control group: received the vehicle alone (23 females) - Analytical verification of doses or concentrations:
- no
- Details on mating procedure:
- - Females were placed with untreated males (1 male: 3 females) overnight and were examined by vaginal smear for the presence of sperm the following morning.
- Sperm-positive females were considered to be in Day 0 of gestation. - Duration of treatment / exposure:
- 15 days (from Gestational Day 6 to GD 20).
- Frequency of treatment:
- daily
- Duration of test:
- around 35 days (1 or 2 weeks' quaranting, mating and gestation)
- Dose / conc.:
- 15 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 25 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 50 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 100 mg/kg bw/day (actual dose received)
- Dose / conc.:
- 200 mg/kg bw/day (actual dose received)
- No. of animals per sex per dose:
- 21 or 23 females per group
- Control animals:
- yes, concurrent vehicle
- Maternal examinations:
- - Maternal observations: daily, for evidence of treatment-related effects.
- Maternal body weight: recorded on day 0 and every 3 days from days 6 to 21 of gestation.
- Food consumption: recorded on days 6, 11, 16 and 21. - Ovaries and uterine content:
- The uterus were removed and weighed. The uterine horns were then opened and the numbers of implantation and resorption sites and of live and dead fetuses were recorded.
- Fetal examinations:
- Live fetuses were removed, weighed, sexed, and examined for external anomalies including those of the oral cavity.
. Half of the viable fetuses from each litter were randomly selected, fixed in Bouin's solution, and examined microscopically as described by Barrow and Taylor for soft tissue anomalies.
. The remaining half of the fetuses were fixed in 70% ethanol and subsequently eviscerated, macerated in 1 % KOH, stained with Alizarin red S, and examined microscopically for skeletal anomalies. - Statistics:
- - Whenever possible, the data were presented as means ± SD.
- Implantation sites, live fetuses and various body weights were analyzed by the one-way analysis of variance, followed by Dunnett's test if differences were found.
- The frequency of nonsurviving implants, resorptions and anomalies among litters was evaluated with the Dixon-Massey test after an arc-sine-square root transformation.
- Rates of pregnancy and fetal sex ratio were analyzed using Fisher's exact test.
- Where applicable, least-squares analysis was carried out. The reported level of statistical significance was p < 0.05. - Clinical signs:
- no effects observed
- Description (incidence and severity):
- No signs of altered behavior or general demeanor were observed among bred rats during gestion.
- Dermal irritation (if dermal study):
- not examined
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- No effect on maternal weight gain was discerned among dams given 15 or 25 mg/kg bw/day. maternal weight gain was significantly depressed over the first 3 days of treatment 50 mg/kg /day, and throughout treatment at 100 and 200 mg/kg bw/day.
Weight gain between Days 6 and 21 of gestation and absolute weight gain were significantly reduced at 50, 100 and 200 mg/kg bw/day. - Food consumption and compound intake (if feeding study):
- not examined
- Food efficiency:
- not examined
- Water consumption and compound intake (if drinking water study):
- not examined
- Ophthalmological findings:
- not examined
- Haematological findings:
- not examined
- Clinical biochemistry findings:
- not examined
- Urinalysis findings:
- not examined
- Behaviour (functional findings):
- not examined
- Immunological findings:
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- not specified
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not specified
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- not examined
- Details on results:
- The pregnancy rates were similar in all groups.
- Number of abortions:
- no effects observed
- Pre- and post-implantation loss:
- not examined
- Total litter losses by resorption:
- no effects observed
- Early or late resorptions:
- no effects observed
- Dead fetuses:
- no effects observed
- Changes in pregnancy duration:
- not examined
- Description (incidence and severity):
- Migrated Data from removed field(s)
Field "Effects on pregnancy duration" (Path: ENDPOINT_STUDY_RECORD.DevelopmentalToxicityTeratogenicity.ResultsAndDiscussion.ResultsMaternalAnimals.MaternalDevelopmentalToxicity.EffectsOnPregnancyDuration): not examined - Changes in number of pregnant:
- no effects observed
- Description (incidence and severity):
- Pegnancy rates were similar in all groups: around 80-90% .
- Other effects:
- not examined
- Details on maternal toxic effects:
- There were no differences among the groups in the mean numbers of implantations and live feuses and in fetal sex ratio when comparent to the control.
There were appearent decreases in the incidences of nonsurviving implants at 25 mg/kg bw/day and of resorptions at 15 and 25 mg/kg bw/day. Review of the control values revealed that these decreases were spuriois and decidely resultated from the high incidences of the concurrent control group. - Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 25 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- Abnormalities:
- no effects observed
- Fetal body weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- DBTU induced a dose-related reduction of fetal weight which was significantly different from the control in females at 15 mg/kg bw/day (6%, reduction, p <0.05), and in males and females at higher dose levels (30% reduction at 200 mg/kg/day) (p< 0.01).
- Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- no effects observed
- Changes in litter size and weights:
- no effects observed
- Changes in postnatal survival:
- no effects observed
- External malformations:
- no effects observed
- Skeletal malformations:
- no effects observed
- Description (incidence and severity):
- The incidences of skeletal variations (primarily reduced ossification of vertebrae and sternebrae and extra lumbar ribs) were similar in all groups of fetuses.
- Visceral malformations:
- no effects observed
- Description (incidence and severity):
- The incidences of visceral variations (primarily dilated renal pelvis and ureter) were similar in all groups of fetuses.
Single instances of omphalocele were observed at 25, 50 and 100 mg/kg/day. The occurrence of this malformation was consistent with the range of incidences seen in historical control litters.
One fetus from control had a diaphragmatic hernia. - Other effects:
- not examined
- Details on embryotoxic / teratogenic effects:
- No differences among the groups in the mean numbers of implantations and live fetuses and in fetal sex ratio when compared to the control.
- Dose descriptor:
- NOAEL
- Remarks:
- teratogenicity
- Effect level:
- > 200 mg/kg bw/day
- Based on:
- test mat.
- Basis for effect level:
- other: No teratogenic effect was observed at any doses.
- Remarks on result:
- not determinable due to absence of adverse toxic effects
- Dose descriptor:
- LOAEL
- Remarks:
- foetotoxicity
- Effect level:
- 15 mg/kg bw/day
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- fetal/pup body weight changes
- Abnormalities:
- not specified
- Developmental effects observed:
- not specified
- Conclusions:
- DBTU was foetotoxic in the absence of distinctive maternal effects. However no teratogenic effects related to administration of DBTU were observed at dose levels up to 200 mg/kg/day, a level which was toxic to the dams.
- Executive summary:
Sprague-Dawley rats were administered 1,3 -dibutyl-2 -thiourea by gavage from Days 6 to 20 of gestation. Daily dosage levels were 0, 15, 25, 50, 100 and 200 mg/kg/day.
No signs of altered or general demeanor were observed among bred rats given DBTU during gestation. No effect on maternal weoght gain was discerned among dams given 15 or 25 mg/kg/day. maternal weight gain was significantly
DBTU was foetotoxic in the absence of distinctive maternal effects. However no teratogenic effects related to administration of DBTU were observed at dose levels up to 200 mg/kg/day, a level which was toxic to the dams. depressed aver the first 3 days of treatment at 50 mg/kg/day, and throughout at 100 and 200 mg/kg/day (p<0.01).Weight gain between Days 6 and 21 of gestation and absolute weight gain were significantly reduced at 50, 100, and 200 mg/kg/day. Pregnancy rates were similar in all groups. There were no differences among the groups in the mean numbers of implantations and live fetuses and in fetal sex ratio when compared to the control. There were apparent decreases in the incidences of nonsurvaving implants at 25 mg/kg/day and of resorptions at 15 and 25 mg/kg/day. Review of the control values revealed that these decreases were spurious and decidely resulted from the high incidences of the concurrent control group. DBTU induced a dose-related reduction of fetal weight which was significantly different from the control in females at 15 mg/kg/day (6%, reduction, p<0.05), and in males and females at higher dose levels (30% reduction at 200 mg/kg/day, p< 0.01). The incidences of visceral variations (primarely dilated renal pelvis and ureter) and skeletal variaations (primarily reduced ossification of vertebrae and sternebrae and extra lumbar ribs) were similar in all groups of fetuses. Single instances of omphalocele were observed at 25, 50 and 100 mg/kg/day. The occurence of this malformation was consistent with the range of incidences seen in historical control litters. One fetus from control had a diaphragmatic hernia.
Reference
Table 1 : Change weigh during gestation in Sprague Dawley rats treated daily by gastric intubation with DBTU
Dose (mg/kg/day) |
Bodyweight on GD6 |
Bodyweight gain (g) |
Absolute weight gain (g) |
|||||
GD 6-9 |
GD 9-12 |
GD 12-15 |
GD 15-18 |
GD 18-21 |
GD 6-21 |
|||
0 |
252 +/- 16 |
15 +/-7 |
19+/-7 |
23+/-7 |
43+/-10 |
55+/-14 |
156 +/-34 |
50+/-12 |
15 |
251+/-19 |
15+/-5 |
15+/-6 |
22+/-4 |
45+/-10 |
53+/-13 |
150+/-25 |
48+/-13 |
25 |
251+/-19 |
12+/-4 |
19+/-5 |
25+/-4 |
44+/-8 |
58+/-10 |
157+/-21 |
46+/-13 |
50 |
248+/-11 |
9+/-5** |
16+/-4 |
20+/-4 |
40+/-6 |
49+/-8 |
133+/-13* |
33+/-13** |
100 |
250+/-11 |
6+/-4** |
18+/-5 |
16+/-4** |
30+/-9** |
45+/-11 |
116+/-26** |
25+/-14** |
200 |
250+/-11 |
0+/-6** |
20+/-9 |
11+/-5** |
24+/-7** |
24+/-18** |
78+/-29** |
-7+/-21** |
* and ** denote significant differences from the vehicle control value using Dunnett’s test, p<0.05 and p<0.01 respectively
Data expressed as means +/- SD
Absolute weight gain = (day 21 body weight) – (gravid uterus weight) – (day 6 body weight)
Table 2: Reproductive parameters in Sprague-Dawley rats treated daily by gastric intubation with DBTU
Dose (mg/kg/day) |
Number of deaths per number of treated females |
Percentage of females pregnant |
Number of examined litters |
Mean implantation sites per litter |
Mean live fetuses per litter |
Mean % nonsurviving implants per litter |
Mean resorptions sites par litter |
Fetal sex ratio M:F (%) |
Mean fetal body weight (g) per litter |
|
males |
females |
|||||||||
0 |
0/23 |
91.3 |
21 |
15.33+/-3.58 |
14.00+/-4.09 |
|
|
0.97 |
5.87+/-0.32 |
5.64+/-0.28 |
15 |
0/23 |
91.3 |
21 |
14.29+/-4.15 |
13.76+/-4.15 |
4.62+/-7.91 |
4.25+/-7.94 |
0.91 |
5.60+/-0.46 |
5.32+/-0.38* |
25 |
0/23 |
95.6 |
22 |
15.77+/-2.43 |
15.36+/-2.59 |
2.85+/-3.68* |
2.60+/-3.48 |
1.05 |
5.44+/-0.26** |
5.15+/-0.24** |
50 |
0/21 |
85.7 |
18 |
15.06+/-1.80 |
14.50+/-1.65 |
3.46+/-5.68 |
3.46+/-5.68 |
0.92 |
5.10+/-0.29** |
4.78+/-0.19** |
100 |
0/21 |
85.7 |
18 |
14.39+/-4.07 |
13.83+/-3.96 |
3.63+/-4.66 |
3.23+/-3.95 |
1.01 |
4.94+/-0.46** |
4.58+/-0.32** |
200 |
0/21 |
81.0 |
17 |
15.29+/-1.21 |
14.53+/-1.37 |
4.89+/-6.49 |
4.89+/-6.49 |
1.13 |
4.12+/-0.45** |
3.97+/-0.47** |
* and ** denote significant differences from the vehicle control value using Dunnett’s test, p<0.05 and p<0.01 respectively
Data expressed as means +/- SD
Table 3: Incidence of anomalies in fetuses of Sprague-Dawley rats treated daily by gastric intubation with DBTU
Doses (mg/kg /day) |
0 |
15 |
25 |
50 |
100 |
200 |
|
Number of fetuses (litters) examined |
|||||
External examination |
294(21) |
289(22) |
338(22) |
261(18) |
249(18) |
247(17) |
Soft tissue examination |
147(21) |
145(21) |
169(22) |
131(18) |
125(18) |
124(17) |
Skeletal examination |
147(20) |
144(22) |
169(22) |
130(18) |
124(17) |
123(17) |
|
Numbers of fetuses (litters) affected |
|||||
External anomalies |
|
|||||
> omphalocele |
0 |
0 |
1(1) |
1(1) |
1(1) |
0 |
> subcutaneous cranial hemorrhage |
0 |
0 |
0 |
0 |
1(1) |
3(2) |
Soft tissue anomalies |
|
|||||
> diaphragmatic hernia |
1(1) |
0 |
0 |
0 |
0 |
0 |
> dilated renal pelvis |
0 |
0 |
0 |
0 |
0 |
8(3) |
> dilated ureter |
0 |
0 |
1(1) |
0 |
1(1) |
4(1) |
Skeletal anomalies |
|
|||||
> interparietal and/or occipital not ossified |
0 |
0 |
0 |
0 |
1(1) |
2(1) |
> vertebral centra dumbbell-shaped or bilobed |
1(1) |
4(4) |
0 |
1(1) |
5(2) |
11(5) |
> ribs wavy |
0 |
1(1) |
0 |
0 |
2(1) |
0 |
> ribs extra cervical |
1(1) |
1(1) |
1(1) |
0 |
0 |
1(1) |
> ribs extra lumbar |
9(7) |
13(7) |
28(11) |
15(11) |
9(7) |
10(5) |
> sternebrae scrambled |
0 |
0 |
0 |
1(1) |
0 |
0 |
> sternebrae fifth not ossified |
0 |
1(1) |
0 |
0 |
1(1) |
3(2) |
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LOAEL
- 15 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- the Saillenfait's study is considered to be reliable with a klimisch score of 2.
Effect on developmental toxicity: via inhalation route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Developmental study in rats (Saillenfait 1991):
Sprague-Dawley rats were administered 1,3 -dibutyl-2 -thiourea by gavage from Days 6 to 20 of gestation. Daily dosage levels were 0, 15, 25, 50, 100 and 200 mg/kg/day.
No signs of altered or general demeanor were observed among bred rats given DBTU during gestation. No effect on maternal weoght gain was discerned among dams given 15 or 25 mg/kg/day. maternal weight gain was significantly depressed aver the first 3 days of treatment at 50 mg/kg/day, and throughout at 100 and 200 mg/kg/day (p<0.01).Weight gain between Days 6 and 21 of gestation and absolute weight gain were significantly reduced at 50, 100, and 200 mg/kg/day. Pregnancy rates were similar in all groups.
There were no differences among the groups in the mean numbers of implantations and live fetuses and in fetal sex ratio when compared to the control. There were apparent decreases in the incidences of nonsurvaving implants at 25 mg/kg/day and of resorptions at 15 and 25 mg/kg/day. Review of the control values revealed that these decreases were spurious and decidely resulted from the high incidences of the concurrent control group. DBTU induced a dose-related reduction of fetal weight which was significantly different from the control in females at 15 mg/kg/day (6%, reduction, p<0.05), and in males and females at higher dose levels (30% reduction at 200 mg/kg/day, p< 0.01).
The incidences of visceral variations (primarely dilated renal pelvis and ureter) and skeletal variaations (primarily reduced ossification of vertebrae and sternebrae and extra lumbar ribs) were similar in all groups of fetuses. Single instances of omphalocele were observed at 25, 50 and 100 mg/kg/day. The occurence of this malformation was consistent with the range of incidences seen in historical control litters. One fetus from control had a diaphragmatic hernia.
DBTU was foetotoxic in the absence of distinctive maternal effects. However no teratogenic effects related to administration of DBTU were observed at dose levels up to 200 mg/kg/day, a level which was toxic to the dams.
Justification for classification or non-classification
Based on the available data, no classification is required for reproduction according to the Regulation EC.N°1272/2008.
Additional information
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