Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 229-494-8 | CAS number: 6574-99-8
- 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
![](https://echa.europa.eu/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Endpoint summary
Administrative data
Description of key information
Acute Oral Toxicity:In an acute oral toxicity study equivalent to OECD 423 the LD50 of 3,4 -Dichlorobenzonitrile was established to be within the range of 200 -2000 mg/kg body weight. Because of this 3,4 -Dichlorobenzonitrile is classified as harmful and requires the hazard statement H302 - "Harmful if swallowed” according to Regulation(EC) No1272/2008.
Acute Dermal Toxicity:
In order to classify the substance 3,4 -Dichlorobenzonitrile (without any unneccessary animal testing) for this enpoint the testing results with 2-Chlorobenzonitrile and 2,6-Dichlorbenzonitrile are read acrossed to 3,4-Dichlorobenzonitrile. 2 -Chlorobenzonitrile was tested in a study equivalent to OECD Guideline 402 to be harmful in contact with skin and was classified as acute tox. 4 H312. This agrees with the official classification in acute dermal toxicity of 2,6 -Dichlorobenzonitrile. Therefore 3,4 -Dichlorobenzonitrile was classified as cute tox. 4 H312 ("Harmful in contact with skin").
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1997-02-11 - 1997-02-27
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 423 (Acute Oral toxicity - Acute Toxic Class Method)
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: Directive 96/54/EC, Part B.1 tris "Acute Toxicity-Oral, Acute Toxic Class Method"
- GLP compliance:
- yes
- Test type:
- acute toxic class method
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Sulzfeld, Germany.
- Age at study initiation: approx. 6 weeks
- Weight at study initiation: within +/- 20 % of the sex mean
- Fasting period before study: food was withheld overnight prior to dosing until approximately 3-4 hours after administration of the test substance.
- Housing: group housing of 3 animals per sex per cage in labelled polycarbonate cages containing purified sawdust as bedding material (Woody SPF, supplied by B.M.I, Helmond, The Netherlands)
- Diet (e.g. ad libitum): free access to standard pelleted laboratory animal diet (from Carfil Quality BVBA, Oud-Turnhout, Belgium)
- Water (e.g. ad libitum): free access to tap-water
- Acclimation period: at least 5 days before start of treatment under laboratory conditions.
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21
- Humidity (%): 50
- Air changes (per hr): 15
- Photoperiod (hrs dark / hrs light): lighting was 12 hours artificial flourescent light and 12 hours dark per day - Route of administration:
- oral: gavage
- Vehicle:
- corn oil
- Details on oral exposure:
- - Method: Oral gavage, using a stainless steel stomach tube.
- Frequency: Once, on day 1.
- Animals: 3 animals of the same sex per dose group. - Doses:
- 200 mg/kg (females), 200 mg/kg (males) and 2000 mg/kg (females)
- No. of animals per sex per dose:
- three
- Control animals:
- no
- Details on study design:
- OBSERVATIONS:
- Mortality/Viability: Twice daily. The time of death was recorded as precisely as possible
- Body weights: Days 1 (pre-administration), 8 and 15 and at death (if found death after day 1).
- Clinical signs: At periodic intervals on the day of dosing (day 1) and once daily thereafter, until day 15. The time of onset, degree and duration were recorded.
- Necropsy of survivors performed: yes - Statistics:
- not performed
- Key result
- Sex:
- female
- Dose descriptor:
- LD50
- Effect level:
- > 200 - < 2 000 mg/kg bw
- Based on:
- test mat.
- Key result
- Sex:
- male
- Dose descriptor:
- LD50
- Effect level:
- > 200 - < 2 000 mg/kg bw
- Based on:
- test mat.
- Mortality:
- All femals dosed at 2000 mg/kg b.w. were found dead within 24 hours of dosing.
- Clinical signs:
- other: 200 mg/kg: Hunched posture, uncoordinated movements. 2000 mg/kg: Lethargy, hunched posture, uncoordinated movements, piloerection. The surviving animals had recovered from symptoms between days 2 and 3. The surviving animals had recovered from the sympto
- Gross pathology:
- No abnormalities were found at macroscopic post mortem examination of the animals.
- Interpretation of results:
- Category 4 based on GHS criteria
- Conclusions:
- The oral LD50 value of 3,4-Dichlorobenzonitrile in Wistar rats was established to be within the range of 200-2000 mg/kg body weight.
According to the EEC criteria for classification and labelling, 3,4-Dichlorobenzonitrile must be classified as harmful if swallowed.
Based on the test result and observation, it can be expected that the classificatoin is also suitable for H302 where 300mg/kg is the threshold. - Executive summary:
The study was carried out based on the guidelines described by oral gavage to three femal Wister rats at 200 mg/kg body weight. In a stepwise procedure additional groups of animals were dosed at 200 (males) and 2000 (females) mg/kg body weight. All animals were subjected to daily observations and weekly determination of body weight. Macroscopic examination was performed on the day of death or after terminal sacrifice 8 (day 15).
All three animals dosed at 2000 mg/kg b.w. were found dead within 24 hours of dosing. The surviving animals recovered from all clinical signs observed between days 2 and 3. The body weight gain shown by the surviving animals over the study period was considered to be normal. No abnormalities were found at macroscopic post mortem examination of the animals.
The oral LD50 value of 3,4 -Dihchlorobenzonitrile in Wistar rats was established to be within the range of 200 -2000 mg/kg body weight.
Reference
The test substance was ranked within LD50 values ranges of 0 - 25, 25 - 200 or 200 - 2000 mg/kg b.w. or as exceeding 2000 mg/kg b.w.
No statistical analysis was performed (The method used is not intended to allow the calculation of a percise LD50 value).
The results were evaluated according to the EEC criteria for classification and labelling requirements for dangerous substances and preparations (Guidelines in Commission Directive 93/21/EEC, 27th april 1993).
Table 1: Body weights of test groups.
Group / Sex |
Animal |
Day 1 [g] |
Day 2 [g] |
Day 8 [g] |
Day 15 [g] |
Group 1 / females |
1 |
126 |
|
179 |
202 |
2 |
131 |
|
171 |
195 |
|
3 |
122 |
|
161 |
170 |
|
Mean |
126 |
|
170 |
189 |
|
St. Dev. |
5 |
|
9 |
17 |
|
N |
3 |
|
3 |
3 |
|
Group 2 / males |
4 |
185 |
|
249 |
283 |
5 |
194 |
|
277 |
309 |
|
6 |
186 |
|
239 |
277 |
|
Mean |
188 |
|
255 |
290 |
|
St. Dev. |
5 |
|
20 |
17 |
|
N |
3 |
|
3 |
3 |
|
Group 3 / females |
7 |
138 |
137 |
- |
- |
8 |
148 |
147 |
- |
- |
|
9 |
143 |
137 |
- |
- |
|
Mean |
143 |
|
- |
- |
|
St. Dev. |
5 |
|
- |
- |
|
N |
3 |
|
0 |
0 |
Table 2: Observed clinical signs of test group 1 (females, 200 mg/kg)
Test day |
1 |
1 |
1 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
||
Time after treatment. hours |
0 |
2 |
4 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||
Animal number |
Signs |
max. grade |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
1 |
gait/motility: uncoordinated movements |
(3) |
- |
1 |
2 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
2 |
gait/motility: uncoordinated movements |
(3) |
- |
1 |
1 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
3 |
Posture: Hunched posture
gait/motility: uncoordinated movements |
(1)
(3) |
-
- |
-
2 |
-
2 |
1
1 |
-
- |
-
- |
-
- |
-
- |
-
- |
-
- |
-
- |
-
- |
-
- |
-
- |
-
- |
-
- |
-
- |
-
- |
Table 3: Observed clinical signs of test group 2 (males, 200 mg/kg)
Test day |
1 |
1 |
1 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
||
Time after treatment. hours |
0 |
2 |
4 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||
Animal number |
Signs |
max. grade |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
4 |
gait/motility: uncoordinated movements |
(3) |
- |
1 |
2 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
5 |
gait/motility: uncoordinated movements |
(3) |
- |
1 |
2 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
6 |
gait/motility: uncoordinated movements |
(3) |
- |
1 |
2 |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
- |
Table 4: Observed clinical signs of test group 3 (females, 2000 mg/kg).
Test day |
1 |
1 |
1 |
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
15 |
||
Time after treatment. hours |
0 |
2 |
4 |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||
Animal number |
Signs |
max. grade |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
7 |
Behavior: Lethargy
Posture: Hunched posture
gait/motility: uncoordinated movements |
(3)
(1)
(3)
|
-
-
- |
-
-
2 |
1
1
2 |
+
+
+ |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
8 |
Posture: Hunched posture
gait/motility: uncoordinated movements |
(1)
(3) |
-
-
|
-
2 |
1
2 |
+
+ |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
9 |
Posture: Hunched posture
gait/motility: uncoordinated movements
Skin /FUR / Plumage: Piloerection |
(1)
(3)
(1) |
-
-
- |
-
2
1 |
1
2
1 |
+
+
+ |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 300 mg/kg bw
- Quality of whole database:
- sufficient
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 2008
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Justification for type of information:
- There is no data available acute dermal toxicity testing with 3,4-Dichlorobenzonitrile. In order to classify the substance according to GHS relevant endpoint data available for 2,6-Dichlorobenzonitrile was read-acrossed to 3,4-Dichlorobenzonitrile based on structural similarities. 2,6-Dichlorobenzonitrile is as well as 3,4-Dichlorobenzonitrile, is a disubstituted Benzonitrile. Both substances only differ in the position of the chloro substituents. Furthermore both substances are solid, practically insoluble in water and have a water octanol partition coefficient of 2.2 and 2.8. This might perhaps also lead to a similiar dermal resorption of the substnces and therefore a similar toxicological behavior. In order to gain more information about 3,4-Dichlorobenzonitrile and to classify the substance (without any unneccessary animal testing) according to GHS the result of the acute dermal test with 2,6-Dichlorbenzonitrile was read acrossed.
For justsification of Read Across see section 13.2 - Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: no guideline rreported
- Principles of method if other than guideline:
- The data was collected from a database only in order to classify the substance.
- GLP compliance:
- not specified
- Key result
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- 1 350 mg/kg bw
- Based on:
- test mat.
- Interpretation of results:
- Category 4 based on GHS criteria
- Executive summary:
There is no data available on dermal toxicity testing with 3,4 -Dichlorobenzonitrile. In order to classify the substance (without any unnecessary animal testing) according to GHS relevant endpoint data for 2,6 -Dichlorobenzonitrile was read-acrossed to 3,4 -Dichlorobenzonitrile based on structural and physico chemical similarities (see rationale for reliability).
2,6 -Dichlorobenzonitrile is officially classified as acute Tox. 4 H312 ("Harmful in contact with skin"). Furthermore a entry in the Chemical Toxicity Database "RTECS number-DI3500000" refers a LD50 value of 1350 mg/kg, which also requires a classification as acute Tox. 4 H312.
Therefore and because of the same classification 2 -Chlorobenzonitrile in dermal toxicity, 3,4 -Dichlorobenzontrile was also classified as acute Tox. 4 H312.
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 1976
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- There is no data available on dermal toxicity testing with 3,4-Dichlorobenzonitrile. In order to classify the substance according to GHS relevant endpoint data available for 2-Chlorobenzonitrile was read-acrossed to 3,4-Dichlorobenzonitrile based on structural and physico chemical similarities. 2-Chlorobenzonitrile, as well as 3,4 -Dichlorobenzonitrile is a Chloro substituted Benzonitrile. Although 2-Chlorobenzonitrile is only monosubstitueted both substances are solid, practically insoluble in water and have similar water octanol partition coefficients (2.2 and 2.8). This might perhaps also lead to a similiar dermal resorption and toxicological behavior.
See also "Justification for Read Across" in Section 13.2 - Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- GLP compliance:
- no
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rabbit
- Strain:
- New Zealand White
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- initial weight: 2.23 - 3.06 kg
- Type of coverage:
- occlusive
- Vehicle:
- propylene glycol
- Details on dermal exposure:
- - The test material was dissoved in propylene glycol
- 9 ml of test dissolved test material contain the applied dose
- Half of the animals received the material on the intact skin, the other half on the abraded skin
- Occlusive conditions: treated area was covered with a thin layer of cellulose sheet and wrapped in polyethylene foil
- After exposure for 24 h the test material was removed with water and the animals were wrapped dry - Duration of exposure:
- 24 hours
- Doses:
- 0, 0.19, 0.34, or 0.6 g/kg body weight
- No. of animals per sex per dose:
- 2 (Half of the animals received the material on the intact skin, the other half on the abraded skin).
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: no data
- Necropsy of survivors performed: yes
- Other examinations performed: clinical signs, body weight,organ weights, histopathology (liver, kidney, spleen, stomach, treated and untreated skin), other: blood composition - Key result
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- >= 340 - <= 600 mg/kg bw
- Based on:
- test mat.
- Mortality:
- 4 (all) animals in the highest dose groupe (600 mg/kg, during teh first days of the observation period); 0 in the 340 mg/kg group, 1 in the 190 mg/kg group (sufferd from diarrhoea and died during teh second week)
- Clinical signs:
- other: During or at the end of the 24-hour exposure period no abnormalities of the treated skin could be observed in any of the test groups. However, all test rabbits were more or less apathetic. In addition the animals of the highest dose group had widened pupi
- Gross pathology:
- Gross and microscopical examination revealed haemorrhagic erosions in the stomach and massive centrolobular liver necrosis in animals of the 0.6 g/kg dose group. Damage of the liver and stomach was obserevd after treatment with 0.6 g/kg body weight. There were no distinct differences in reactions either between rabbits treated on the intact or abraded skin or between male and female rabbits.
- Other findings:
- - Haemoglobin content of the blood and red blood cell counts of rabbits of the 0.34 g/kg dose group were slightly higher than those of control rabbits. Those differences are not considered to be of toxicological significance since values are within the normal range.
- At autopsy, groes examination of the rabbits of the highest dose group, which died during the experiment, revealed haemorrhagic erosions in the stomach of three rabbits. The animal of the lowest dose group that died and the rabbits that survived the experiment did not show macroscopic changes attributable to treatment.
- microscopical examination revealed treatment-related changes in the liver and stomach. Two rabbits of the highest dose group showed massive centrilobular liver necrosis, while small foci of centrilobular liver necrosis were observed in one rabbit of each test group. It is not clear whether these liver injuries are the result of a direct toxic action of the test compound or of an indirect effect resulting from anoxia.
- Three rabbits of the highest doce group showed haemorrhagic erosions in the fundic part of the stomach, which was considered to be due to preterminal conditional decline.
- Other abnormalities in liver, kidneys, heart and the treated skin occurred to about the sarme degree and frequency in test and control animals or occurred in a single rabbit and are, therefore, not considered te be of toxicological significance. - Interpretation of results:
- Category 4 based on GHS criteria
- Conclusions:
- The dermal LD50 of 2-Chlorobenzonitrile is between 340 and 600 mg/kg bw in rabbits under conditions of this study.
It should be noted that resorption of the test substance has probably been enhanced due to the application in propylene glycol. Therefore, 2-Chlorobenzonitrile is not classified as H311 ("Toxic in contact with skin") but H312 ("Harmful in contact with skin"). - Executive summary:
The acute dermal toxicity of 2-Chlorobenzonitrile was examined in an experiment with 8 adult New Zealand White Rabbits/sex/dose. The animals were treated with 2-Chlorobenzonitrile dissolved in propylene glycol at dose levels of 0, 0.19, 0.34 or 0.6 g/kg body weight for 24h. Half the number of animals received the material on the intact skin, the other half on abraded skin.
The dermal application caused apathy of the rabbits in all test groups and widened pupils, tremors and paresis or paralysis in the highest dose group. All animals of the highest dose group died during the first days. The animals of the other groups recovered completely, except one rabbit of the 0.19 g/kg dose group that suffered from diarrhoea and died during the second week of the observatiuon period.
The dermal LD50 of 2 -Chlorobenzonitrile was concluded to be between 340 and 600 mg/kg bw.
It should be noted that resorption of the test substance has probably been enhanced due to the application in propylene glycol. Therefore, 2-Chlorobenzonitrile is not classified as H311 ("Toxic in contact with skin") but H312 ("Harmful in contact with skin").
As there is no data available on dermal toxicity testing with 3,4 -Dichlorobenzonitrile relevant endpoint data available for 2 -Chlorobenzonitile was read-acrossed to 3,4 -Dichlorobenzonitrile in order to classify the substance (without any unecessary animal testing) according to GHS. The Read-Across approach was based on structural and physico chemical similarities (see rational for reliability).
2 -Chlorobenzonitrile was tested in a study equivalent to OECD Guideline 402 (Acute Dermal Toxicity) to be harmful in contact with skin and was classfied as acute tox. 4 H312. This agrees with the official classification in acute dermal toxicity of 2,6 -Dichlorobenzonitrile. Therefore 3,4 -Dichlorobenzonitrile was classified as acute Tox. 4 H312 ("Harmful in contact with skin".)
- Endpoint:
- acute toxicity: dermal
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Study period:
- 2008
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Justification for type of information:
- here is no data available acute dermal toxicity testing with 3,4-Dichlorobenzonitrile. In order to classify the substance according to GHS relevant endpoint data available for 2,6-Dichlorobenzonitrile was read-acrossed to 3,4-Dichlorobenzonitrile based on structural similarities. 2,6-Dichlorobenzonitrile is as well as 3,4-Dichlorobenzonitrile, is a disubstituted Benzonitrile. Both substances only differ in the position of the chloro substituents. Furthermore both substances are solid, practically insoluble in water and have a water octanol partition coefficient of 2.2 and 2.8. This might perhaps also lead to a similiar dermal resorption of the substnces and therefore a similar toxicological behavior. In order to gain more information about 3,4-Dichlorobenzonitrile and to classify the substance (without any unneccessary animal testing) according to GHS the result of the acute dermal test with 2,6-Dichlorbenzonitrile was read acrossed.
See also Justification for Read Across in Section 13.2 - Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- other: no guidline reported
- Principles of method if other than guideline:
- The data was collected from a database only in order to classify the substance.
- GLP compliance:
- not specified
- Key result
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- 1 350 mg/kg bw
- Based on:
- test mat.
- Interpretation of results:
- Category 4 based on GHS criteria
- Executive summary:
There is no data available on dermal toxicity testing with 3,4 -Dichlorobenzonitrile. In order to classify the substance (without any unnecessary animal testing) according to GHS relevant endpoint data for 2,6 -Dichlorobenzonitrile was read-acrossed to 3,4 -Dichlorobenzonitrile based on structural and physico chemical similarities (see rationale for reliability).
2,6 -Dichlorobenzonitrile is officially classified as acute Tox. 4 H312 ("Harmful in contact with skin"). Furthermore a entry in the Chemical Toxicity Database "RTECS number-DI3500000" refers a LD50 value of 1350 mg/kg, which also requires a classification as acute Tox. 4 H312.
Therefore and because of the same classification 2 -Chlorobenzonitrile in dermal toxicity, 3,4 -Dichlorobenzontrile was also classified as acute Tox. 4 H312.
- Endpoint:
- acute toxicity: dermal
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Study period:
- 1976
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- There is no data available on dermal toxicity testing with 3,4-Dichlorobenzonitrile. In order to classify the substance according to GHS relevant endpoint data available for 2-Chlorobenzonitrile was read-acrossed to 3,4-Dichlorobenzonitrile based on structural and physico chemical similarities. 2-Chlorobenzonitrile, as well as 3,4 -Dichlorobenzonitrile is a Chloro substituted Benzonitrile. Although 2-Chlorobenzonitrile is only monosubstitueted both substances are solid, practically insoluble in water and have similar water octanol partition coefficients (2.2 and 2.8). This might perhaps also lead to a similiar dermal resorption and toxicological behavior.
See also "Justification for Read Across" in Section 13.2 - Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 402 (Acute Dermal Toxicity)
- GLP compliance:
- no
- Test type:
- standard acute method
- Limit test:
- no
- Species:
- rabbit
- Strain:
- New Zealand White
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- initial weight: 2.23 - 3.06 kg
- Type of coverage:
- occlusive
- Vehicle:
- propylene glycol
- Details on dermal exposure:
- - The test material was dissoved in propylene glycol
- 9 ml of test dissolved test material contain the applied dose
- Half of the animals received the material on the intact skin, the other half on the abraded skin
- Occlusive conditions: treated area was covered with a thin layer of cellulose sheet and wrapped in polyethylene foil
- After exposure for 24 h the test material was removed with water and the animals were wrapped dry - Duration of exposure:
- 24 hours
- Doses:
- 0, 0.19, 0.34, or 0.6 g/kg body weight
- No. of animals per sex per dose:
- 2 (Half of the animals received the material on the intact skin, the other half on the abraded skin).
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Duration of observation period following administration: 14 days
- Frequency of observations and weighing: no data
- Necropsy of survivors performed: yes
- Other examinations performed: clinical signs, body weight,organ weights, histopathology (liver, kidney, spleen, stomach, treated and untreated skin), other: blood composition - Key result
- Sex:
- male/female
- Dose descriptor:
- LD50
- Effect level:
- >= 340 - <= 600 mg/kg bw
- Based on:
- test mat.
- Mortality:
- 4 (all) animals in the highest dose groupe (600 mg/kg, during teh first days of the observation period); 0 in the 340 mg/kg group, 1 in the 190 mg/kg group (sufferd from diarrhoea and died during teh second week)
- Clinical signs:
- other: During or at the end of the 24-hour exposure period no abnormalities of the treated skin could be observed in any of the test groups. However, all test rabbits were more or less apathetic. In addition the animals of the highest dose group had widened pupi
- Gross pathology:
- Gross and microscopical examination revealed haemorrhagic erosions in the stomach and massive centrolobular liver necrosis in animals of the 0.6 g/kg dose group. Damage of the liver and stomach was obserevd after treatment with 0.6 g/kg body weight. There were no distinct differences in reactions either between rabbits treated on the intact or abraded skin or between male and female rabbits.
- Other findings:
- - Haemoglobin content of the blood and red blood cell counts of rabbits of the 0.34 g/kg dose group were slightly higher than those of control rabbits. Those differences are not considered to be of toxicological significance since values are within the normal range.
- At autopsy, groes examination of the rabbits of the highest dose group, which died during the experiment, revealed haemorrhagic erosions in the stomach of three rabbits. The animal of the lowest dose group that died and the rabbits that survived the experiment did not show macroscopic changes attributable to treatment.
- microscopical examination revealed treatment-related changes in the liver and stomach. Two rabbits of the highest dose group showed massive centrilobular liver necrosis, while small foci of centrilobular liver necrosis were observed in one rabbit of each test group. It is not clear whether these liver injuries are the result of a direct toxic action of the test compound or of an indirect effect resulting from anoxia.
- Three rabbits of the highest doce group showed haemorrhagic erosions in the fundic part of the stomach, which was considered to be due to preterminal conditional decline.
- Other abnormalities in liver, kidneys, heart and the treated skin occurred to about the sarme degree and frequency in test and control animals or occurred in a single rabbit and are, therefore, not considered te be of toxicological significance. - Interpretation of results:
- Category 4 based on GHS criteria
- Conclusions:
- The dermal LD50 of 2-Chlorobenzonitrile is between 340 and 600 mg/kg bw in rabbits under conditions of this study.
It should be noted that resorption of the test substance has probably been enhanced due to the application in propylene glycol. Therefore, 2-Chlorobenzonitrile is not classified as H311 ("Toxic in contact with skin") but H312 ("Harmful in contact with skin"). - Executive summary:
The acute dermal toxicity of 2-Chlorobenzonitrile was examined in an experiment with 8 adult New Zealand White Rabbits/sex/dose. The animals were treated with 2-Chlorobenzonitrile dissolved in propylene glycol at dose levels of 0, 0.19, 0.34 or 0.6 g/kg body weight for 24h. Half the number of animals received the material on the intact skin, the other half on abraded skin.
The dermal application caused apathy of the rabbits in all test groups and widened pupils, tremors and paresis or paralysis in the highest dose group. All animals of the highest dose group died during the first days. The animals of the other groups recovered completely, except one rabbit of the 0.19 g/kg dose group that suffered from diarrhoea and died during the second week of the observatiuon period.
The dermal LD50 of 2 -Chlorobenzonitrile was concluded to be between 340 and 600 mg/kg bw.
It should be noted that resorption of the test substance has probably been enhanced due to the application in propylene glycol. Therefore, 2-Chlorobenzonitrile is not classified as H311 ("Toxic in contact with skin") but H312 ("Harmful in contact with skin").
As there is no data available on dermal toxicity testing with 3,4 -Dichlorobenzonitrile relevant endpoint data available for 2 -Chlorobenzonitile was read-acrossed to 3,4 -Dichlorobenzonitrile in order to classify the substance (without any unecessary animal testing) according to GHS. The Read-Across approach was based on structural and physico chemical similarities (see rational for reliability).
2 -Chlorobenzonitrile was tested in a study equivalent to OECD Guideline 402 (Acute Dermal Toxicity) to be harmful in contact with skin and was classfied as acute tox. 4 H312. This agrees with the official classification in acute dermal toxicity of 2,6 -Dichlorobenzonitrile. Therefore 3,4 -Dichlorobenzonitrile was classified as acute Tox. 4 H312 ("Harmful in contact with skin".)
Referenceopen allclose all
Table – individual body weight
number |
sex |
Dose (mg/kg) |
Condition of skin |
Body weight day 0 (kg) |
Body weight end of week 1 (kg) |
Body weight end of week 2 (kg) |
3638 |
M |
0 |
abraded |
3.06 |
3.09 |
3.36 |
3639 |
M |
0 |
intact |
2.60 |
2.55 |
2.78 |
3627 |
F |
0 |
abraded |
2.93 |
2.88 |
3.13 |
3625 |
F |
0 |
intact |
2.93 |
2.30 |
2.45 |
3641 |
M |
190 |
abraded |
3.05 |
3.07 |
3.32 |
3644 |
M |
190 |
intact |
2.45 |
2.43 |
2.82 |
3662 |
F |
190 |
abraded |
2.55 |
1.77 |
dead |
3663 |
F |
190 |
intact |
2.70 |
2.68 |
3.00 |
3645 |
M |
340 |
abraded |
2.65 |
2.83 |
2.82 |
3646 |
M |
340 |
Intact |
3.05 |
3.00 |
3.36 |
3660 |
F |
340 |
abraded |
2.62 |
2.85 |
3.15 |
3661 |
F |
340 |
intact |
2.32 |
2.50 |
3.02 |
3635 |
M |
600 |
abraded |
3.05 |
dead |
dead |
3637 |
M |
600 |
intact |
2.61 |
dead |
dead |
3621 |
F |
600 |
abraded |
2.88 |
dead |
dead |
3622 |
F |
600 |
intact |
2.36 |
dead |
dead |
Table – individual body weight
number |
sex |
Dose (mg/kg) |
Condition of skin |
Body weight day 0 (kg) |
Body weight end of week 1 (kg) |
Body weight end of week 2 (kg) |
3638 |
M |
0 |
abraded |
3.06 |
3.09 |
3.36 |
3639 |
M |
0 |
intact |
2.60 |
2.55 |
2.78 |
3627 |
F |
0 |
abraded |
2.93 |
2.88 |
3.13 |
3625 |
F |
0 |
intact |
2.93 |
2.30 |
2.45 |
3641 |
M |
190 |
abraded |
3.05 |
3.07 |
3.32 |
3644 |
M |
190 |
intact |
2.45 |
2.43 |
2.82 |
3662 |
F |
190 |
abraded |
2.55 |
1.77 |
dead |
3663 |
F |
190 |
intact |
2.70 |
2.68 |
3.00 |
3645 |
M |
340 |
abraded |
2.65 |
2.83 |
2.82 |
3646 |
M |
340 |
Intact |
3.05 |
3.00 |
3.36 |
3660 |
F |
340 |
abraded |
2.62 |
2.85 |
3.15 |
3661 |
F |
340 |
intact |
2.32 |
2.50 |
3.02 |
3635 |
M |
600 |
abraded |
3.05 |
dead |
dead |
3637 |
M |
600 |
intact |
2.61 |
dead |
dead |
3621 |
F |
600 |
abraded |
2.88 |
dead |
dead |
3622 |
F |
600 |
intact |
2.36 |
dead |
dead |
Endpoint conclusion
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 350 mg/kg bw
Additional information
Justification for classification or non-classification
Acute Oral Toxicity: In an acute oral toxicity study equivalent to OECD 423 the LD50 of 3,4 -Dichlorobenzonitrile was established to be within the range of 200 -2000 mg/kg body weight. Because of this 3,4 -Dichlorobenzonitrile is classified as harmful and requires the hazard statement H302 - "Harmful if swallowed” according to Regulation(EC) No1272/2008.
Acute Dermal Toxicity:
There is no data available on dermal toxicity studies with 3,4-Dichlorobenzonitrile. In order to classify the substance according to GHS relevant endpoint data available for 2-Chlorobenzonitrile and 2,6-Dichlorobenzonitrile was read-acrossed to 3,4-Dichlorobenzonitrile based on structural and physico chemical similarities.
2,6-Dichlorobenzonitrile, as well as 3,4 -Dichlorobenzonitrile is a disubstituted Benzonitrile. Both substances only differ in the position of the chloro substituents. 2-Chlorobenzonitile is a next lower homologon of 2,6-Dichlorobenzonitrile. Furthermore all three substances are solid, practically insoluble in water and have a water octanol partition coefficient between 2.2 and 2.8. This might perhaps also lead to a similiar toxicological behavior. The Read-Across approach assumes that if a Monochlorobenzonitrile and a Dichlorobenzonitril show similiar toxicological behavior, it is likely that a second Dichlorobenzonitril also shows this similar behavior. Particularly if it has the same physico chemical properties like practically insoluble in water and logKow between 2.2 and 2.8, which might lead to a comparable dermal resorption of the substances.
In order to classify the substance 3,4 -Dichlorobenzonitrile (without any unneccessary animal testing) for this enpoint the testing results with 2-Chlorobenzonitrile and 2,6-Dichlorbenzonitrile are read acrossed to 3,4-Dichlorobenzonitrile. 2 -Chlorobenzonitrile was tested in a study equivalent to OECD Guideline 402 to be harmful in contact with skin and was classified as acute tox. 4 H312. This agrees with the official classification in acute dermal toxicity of 2,6 -Dichlorobenzonitrile. Therefore 3,4 -Dichlorobenzonitrile was classified as cute tox. 4 H312 ("Harmful in contact with skin").
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
![ECHA](/o/diss-blank-theme/images/factsheets/A-REACH/factsheet/echa_logo.png)