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EC number: 931-297-3 | CAS number: -
- 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
Developmental toxicity / teratogenicity
Administrative data
- Endpoint:
- developmental toxicity
- Type of information:
- migrated information: read-across based on grouping of substances (category approach)
- Adequacy of study:
- key study
- Study period:
- 2003-10-14 to 2004-11-09
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: According to ECHA Practical Guide 6 the maximum score for read across is rel. 2
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 004
- Report date:
- 2004
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- GLP compliance:
- yes
- Limit test:
- no
Test material
- Reference substance name:
- 3-isocyanatomethyl-3,5,5-trimethylcyclohexyl isocyanate
- EC Number:
- 223-861-6
- EC Name:
- 3-isocyanatomethyl-3,5,5-trimethylcyclohexyl isocyanate
- Cas Number:
- 4098-71-9
- IUPAC Name:
- 5-isocyanato-1-(isocyanatomethyl)-1,3,3-trimethylcyclohexane
- Details on test material:
- isophorone diisocyanate of Bayer Polymers, batch no. LL48/3-55, purity 99.8 %, sampled 07 Aug 2003
Constituent 1
Test animals
- Species:
- rat
- Strain:
- Wistar
- Details on test animals or test system and environmental conditions:
- TEST ORGANISMS
- Source: Hsd Cpb:WU from Harlan-Winkelmann GmbH, Borchen (Germany)
- Age: between 14 and 17 weeks (females)
- Weight at study initiation: 201 - 244 g (females)
- Number of animals: 27 per dose / control group
Housing conditions:
- Room temperature: 22°C+/-2°C;
- humidity: appr. 50%;
- light: 12hours light/dark;
- air change: 10 times per hour;
- animal room was cleaned daily
- nutrition: standard diet Provimi Kliba Maus/Ratte-Haltung-GLP, Art.-No 3883.0.15 (Provimi Kliba SA, 4303 Kaiseraugst, Switzerland) ad libitum
- water: tap water ad libitum
Administration / exposure
- Route of administration:
- inhalation
- Type of inhalation exposure (if applicable):
- nose only
- Vehicle:
- other: air
- Details on exposure:
- Females:
- exposure by inhalation (nose only) daily from day 6 to 19 post coitum for 6 hours between approximately 08:00 and 14:00 CET.
Males:
- not treated (used only for mating) - Analytical verification of doses or concentrations:
- yes
- Details on analytical verification of doses or concentrations:
- Doses used in this study were verified by analysis. The analyses of the test atmospheres are described in the analytical report (study no. T 7072620) which is part of the main study. The test atmosphere was determined by high performance liquid chromatography (HPLC) after derivatization of the
isocyanate functionality. Samples were taken by using glass powder filled tubes containing nitro-reagent as scavenging agent. For
reference/calibration purposes the test compund was used. The precision, accuracy and stability in solvents as well as on the adsorbent used were
checked prior to the study. Chamber samples were taken in the vicinity of the breathing zone. - Details on mating procedure:
- MATING PROCEDURES:
Two females and one male were placed in a cage overnight. If sperm was detected in the vaginal smear taken in the morning, this day was
regarded as day 0 of gestation. - Duration of treatment / exposure:
- days 6 through 19 post coitum
- Frequency of treatment:
- 6 hours/day, daily
- Duration of test:
- The femals were subjected to gross pathological examination at the time of cesarian section on day 20 post coitum. The females were sacrificed using cardiotomy under deep carbon dioxide anesthesia.
Doses / concentrationsopen allclose all
- Remarks:
- Doses / Concentrations:
0 (air control); 0.25; 1.0; 4.0 mg/m3
Basis:
other: target concentration
- Remarks:
- Doses / Concentrations:
--; 1.1; 5.0; 23.6 mg/m3
Basis:
nominal conc.
- Remarks:
- Doses / Concentrations:
--; 0.206; 0.929; 4.536 mg/m3
Basis:
analytical conc.
- No. of animals per sex per dose:
- 27 inseminated females per dose
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- Sex: female
Duration of test: cesarean section on day 20
Examinations
- Maternal examinations:
- PARAMETERS ASSESSED DURING STUDY:
- Mortality: daily on days 0 through 5 and 20, twice daily on days 6 through 19
- Clinical signs: daily on days 0 through 5 and 20, twice daily on days 6 through 19
- Body weight gain: Weighing on days 0 and 6 through 20, correction for weight of uterus on day 20
- Food consumption: Cumulative on days 3, 6, 9, 12, 15, 18, and 20; water consumption 3 times/week - Ovaries and uterine content:
- - Examination of uterine content:
Number of corpora lutea, number of implantations (in females without visible implantation sites after staining with 10 % ammonium sulfide
solution), uterine weights, individual weight and appearance of the placentas, number of early resorptions (only implantation sites visible),
number of late resorptions (fetal or placental remnant visible), number of dead fetuses (i.e. without signs of life, without maceration), number and sex of live fetuses - Fetal examinations:
- - Examination of fetuses: sex, individual weight, external malformations or other findings deviating from normal, visceral malformations and other
findings deviating from normal (Wilson technique), findings in abdominal, pelvic, and thoracic organs as well as skeletal and cartilage findings
(modified Dawson technique) with the addition of cartilage staining: evisceration, cartilage staining with alcian blue GX, clearing of the fetuses
with diluted potassium hydroxide solution, staining of the skeletal system with alizarin red S and evaluation of the skeletal system including
cartilaginous findings. Every other fetus within a litter was prepared for either skeletal or visceral evaluation with generally the first fetus of
each litter assigned to skeletal analysis. - Statistics:
- STATISTICAL METHODS:
- Females without implanatation sites were excluded. Skeletal localizatins with mechanical damage in single fetuses were excluded from the
calculation of percentages of affected localizations but reported in the tables of individual skeletal findings.
- Analysis of variance, and in case of significant results Dunnett's test for: feed consumption; body weights (incl. gains and corrections);
uterine weights; number of corpora lutea, of implantations, of live fetuses (incl. percentages) per female; placental and fetal weights per female.
- 2 by N Chi(square) test, and in case of significant differences Fisher's exact test with Bonferroni correction for: fertility and gestation rate;
number of implantations per group; number of preimplantation losses per group; number of postimplantation losses, early resorptions, late
resorptions, or dead fetuses per group; number of live fetuses per group in percent of implantations; number of male or female fetuses or fetuses with undeterminable sex per group; number of fetuses or litters with external, visceral, and skeletal findings; number of fetuses or litters with
malformations.
- Kruskal-Wallis test, and in case of significant differences Dunn's test for: number of preimplantation losses, postimplantation losses, early
resorptions, late resorptions or dead fetuses per female; number of male or female fetuses or fetuses with undeterminable sex per female;
proportin of placental, fetal external, and fetal visceral findings per female.
- Chi(square) test (correction according to Yates) for: number of
fetuses or litters with cartilaginous tissue observations. - Indices:
- For external, skeletal and visceral malformations a scheme for classification and an incidence table is described within the study.
- Historical control data:
- Description of historical control data is part of the study report (annex) for e.g.: vehicles, clinical findings, feed consumption, body weight gain,
gross pathological findings, fertility and gestation index, total resorptions, Cesarean section data, placental findings, number of malformations,
spontaneous malformations, external and visceral deviations, skeletal findings in fetuses and litters (including cartilaginous findings), incidence of
eye malformations in different historical dose groups
Results and discussion
Results: maternal animals
Maternal developmental toxicity
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
No mortalities were reported. Treatment with the test substance Isophorondiisocyanat (IPDI) at the 4 mg/m3 exposure level affected the respiratory tract and the fur and comprised decreased respiratory rate (bradypnea), laboured breathing, breathing sounds, reddish encrusted nostrils, serous nasal discharge and rough fur. Furthermore, decreased feed intake, body weight loss for 2 days and impaired body weight gain was evident in the 4 mg/m3 exposure group. Necropsy revealed no treatment related gross pathological findings at an exposure level up to and including 4 mg/m3.
Effect levels (maternal animals)
open allclose all
- Dose descriptor:
- NOAEC
- Effect level:
- 1 mg/m³ air
- Basis for effect level:
- other: maternal toxicity
- Dose descriptor:
- NOAEC
- Effect level:
- 1 mg/m³ air
- Basis for effect level:
- other: developmental toxicity
- Dose descriptor:
- NOAEC
- Effect level:
- 0.929 mg/m³ air (analytical)
- Basis for effect level:
- other: maternal toxicity
- Dose descriptor:
- NOAEC
- Effect level:
- 0.929 mg/m³ air (analytical)
- Basis for effect level:
- other: developmental toxicity
Results (fetuses)
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:yes
Details on embryotoxic / teratogenic effects:
Reduction of fetal weight was evident in the 4 mg/m3 group and treatment relationship could not be completely excluded for marginally impaired
placental weight at the 4 mg/m3 exposure level. A treatment related effect on the incidence and type of fetal malformations was not assumed at an
exposure level up to and including 4 mg/m3. Slightly retarded ossification of few localizations (phalanges, sternebrae, sacral and caudal vertebrae)
was assumed and slightly impaired descensus testi could not be completely excluded at the 4 mg/m3 exposure level in relation to decreased fetal
weights and dose dependency. All signs of developmental toxicity observed at the 4 mg/m3 exposure level i.e. reduced fetal weight, delayed
descensus testis and slightly retarded ossification were indicative of delayed fetal development and were only seen in the presence of maternal
toxicity and thus considered a secondary effect.
Fetal abnormalities
- Abnormalities:
- not specified
Overall developmental toxicity
- Developmental effects observed:
- not specified
Any other information on results incl. tables
For developmental toxicity a read across to HDI oligomers, isocyanurate type (EC 931 -274 -8) is applied. This substance is a close structural analogue to HDI oligomers, iminooxadiazindione type, also derived from catalytic oligomerisation of 1,6 -hexamethylene diisocyanate (HDI; CAS 822 -06 -0) and also belonging to the CAS number 28182-81-2 (Hexane, 1,6 - diisocyanato-, homopolymer).The read across is based on physicochemical and toxicological similarity. In fact, comparison of the toxicological endpoints, that are available for both of the two substances (Acute oral toxicity, Acute inhalation toxicity, Skin and Eye Irritation/Corrosion, Skin Sensitisation, Bacterial mutagenicity (Ames)) reveal good correlation. With respect to Inhalation Toxicity an expert statement is available justifying the read across (Pauluhn, Comparison of pulmonary irritation potency..., Bayer HealthCare AG, 2008).
Therefore, all available toxicological data for HDI oligomers, isocyanurate type can be used for the toxicological evaluation of HDI oligomers, iminooxadiazindione type and all waiving conclusions drawn for HDI oligomers, isocyanurate type are also valid for HDI oligomers, iminooxadiazindione type. This approach is in accordance with Annex XI, section 1.5 of the REACH Regulation (Regulation (EC) No 1907/2006).
Comments for IPDI:
Result: not teratogenic
ACTUAL DOSE RECEIVED BY DOSE LEVEL BY SEX: Chemical analyses demonstrated satisfactory stability and agreement
between nominal and actual concentrations of the test material.
MATERNAL TOXIC EFFECTS BY DOSE LEVEL:
- Mortality and day of death: No mortalities were reported.
- Description, severity, time of onset and duration of clinical signs: decreased respiratory rate (bradypnea), labored breathing,
breathing sounds, reddish encrusted nostrils, serous nasal discharge, rough fur (4 mg/m3 group). Effects on breathing as well as
nasal discharge were not observed in the other groups, while effects on nose and nostrils were rare (maximum 2 females/group)
and likely related to restraint. Rough fur occurred in some females of all study groups, including the control group, but showed a
sharp increase in incidence with the 4 mg/m3 group.
- Food/water consumption: Decreased feed intake throughout the exposure period was observed in the 4 mg/m3 group
(14.7 %
below control; p < 0.01) and during the last interval (days 18-20) in the 0.25 mg/m3 group (p < 0.05, not dose related). After
start of inhalation, reduced feed intake was observed in all study groups including control, most probably due to the inhalation
procedure. Beyond this, feed intake was normal. No effects on water intake and on excretion of urine and feces were observed in
any group.
- Body weight: The body weight in the 4 mg/m3 group from day 0 to day 20 was lower by 7.9 %, the corrected body weight
(body weight minus unterine weight) was lower by 9.2 %. The body weight gain in the 4 mg/m3 group from day 0 to day 20 was
lower by 23.5 % (absolute; relative to initial weight: -21.7 %; corrected: -91.3 %; compared to control; p < 0.01). After start of
inhalation, body weight loss was observed in all study groups including control, most probably due to the inhalation procedure.
Beyond this, body weight development was normal.
- Gross pathology incidence and severity: There were no treatment related gross pathological findings in any group.
- Number pregnant per dose level: control: 24/27; 0.25 mg/m3: 23/27; 1 mg/m3: 24/27; 4 mg/m3: 26/27
- Number of implantations: control 11.9; 0.25 mg/m3: 11.9; 1 mg/m3: 13.0, 4 mg/m3: 12.0 (mean per female with implantation sites)
= no significant differences
- Pre and post implantation loss: control: 1.7 / 0.8; 0.25 mg/m3: 2.1 / 0.7; 1 mg/m3: 1.2 / 0.7; 4 mg/m3: 1.4 / 0.5
(mean pre- / postimplantation loss per female with implantation sites) = no significant differences
- Number of corpora lutea: control: 13.6; 0.25 mg/m3: 14.0; 1 mg/m3: 14.1, 4 mg/m3: 13.4 (mean per female with implantation sites)
= no significant differences
- Number aborting: No abortion in any group
- Number of resorptions: There were no females with total resorption in any group.
- Duration of pregnancy: determined by cesarean section on day 20
- Other findings: Placental weights were marginally decreased at the 4 mg/m3 level (-6.6 %, not statistically significant but slightly
below historical control data range).
FETAL DATA:
- Litter size and weights: mean fetal weight in control: 3.51 g; 0.25 mg/m3: 3.49 g; 1 mg/m3: 3.46 g; 4 mg/m3: 3.27 g, i.e. reduction
of fetal weight in 4 mg/m3 group (-6.8 %; p < 0.01)
- Number viable: control: 11.1; 0.25 mg/m3: 11.2; 1 mg/m3: 12.3; 4 mg/m3: 11.5, i.e. no treatment related findings
- Sex ratio: control: 49.3; 0.25 mg/m3: 48.3; 1 mg/m3: 50.0; 4 mg/m3: 52.0 % males, i.e. no treatment related findings
- Grossly visible abnormalities: There is no evidence for treatment relation. A marginally higher number of common eye
malformations in the 4 mg/m3 group (1 % of the fetuses and 7.7 % of litters affected vs. 0.4 % of fetuses and 4.2 % of litters in
control), which is well within the range of historical control data (up to 1.8 % of fetuses and 20 % of litters affected), is
considered to be either incidental or secondary (reduced oxygen supply to offspring by maternal bradypnea).
control: 1.1 % of fetuses / 12.5 % of litters showed malformations
0.25 mg/m3: 1.6 % of fetuses / 13.0 % of litters showed malformations
1.0 mg/m3: 2.0 % of fetuses / 20.8 % of litters showed malformations
4.0 mg/m3: 1.7 % of fetuses / 11.5 % of litters showed malformations
- External abnormalities: External deviations were not observed in this study.
- Soft tissue abnormalities: Statistical significance was only evident for reduced number of tracheal findings (membraneous part of
trachea slightly folded, lying in tracheal lumen; possibly of artefactual origin) in the 1 mg/m3 and 4 mg/m3 groups and for reduced
total number of fetuses with deviations in the 1 mg/kg exposure group. Based on lack of dose relationship (control: 23; 0.25 mg/m3:
11; 1 mg/m3: 6; 4 mg/m3: 10 %), highest incidence of the tracheal finding in the actual control group and lack of pathological
significance per se for a reduced number, these findings were considered incidental. Other deviations observed during visceral
evalution were either common or without dose relationship. In conclusion, an effect on incidence and type of external and visceral
deviations was not evident at an exposure level up to and including 1 mg/m3, while slightly retarded descensus testis (4 % of fetuses
and 38.5 % of litters vs. 2.2 % of fetuses and 25 % of litters in the control group) was observed at the maternally toxic 4 mg/m3
exposure level. In relation to decreased fetal weights treatment relationships could not be totally excluded, although the individual
alterations lay well in the range of historical data and statistical significance was not evident.
control: 27.0 % of fetuses / 95.8 % of litters showed deviations
0.25 mg/m3: 24.4 % of fetuses / 87.0 % of litters showed deviations
1.0 mg/m3: 17.0 % of fetuses / 87.5 % of litters showed deviations
4.0 mg/m3: 23.0 % of fetuses / 96.2 % of litters showed deviations
- Skeletal abnormalities: Fetal skeletal including cartilaginous tissue evaluation for degree of ossification and
incidence of variations relealed no toxicologically relevant effects at an exposure level up to and including 1 mg/m3. Dose relation
was missing for all findings at 0.25 and 1 mg/m3, and statistical significance was absent either on a fetus base, or on a litter base,
or for both. Statistically significant fetal skeletal findings at the 4 mg/m3 exposure level included retarded ossification of distal and
proximal phalanges of digits and toes, of metacarpal bones, 6th sternal segment, 7th cervical vertebral body, sacral and caudal
vertebral arches and caudal vertebral bodies. Incidence of findings at the proximal phalanges of digits and distal phalanges of toes,
of metacarpals, and sacral and caudal vertebrae lay outside the range of recent historical control data on a fetal basis, and although
statistical significance on a litter basis was restricted to delayed ossification of proximal phalanges of digits, treatment relationship
was assumed for retarded ossification of these localizations in relation to as well impaired fetal weight. Other findings in the
4 mg/m3 group were considered to be of no toxicological relevance.
Applicant's summary and conclusion
- Conclusions:
- Animals treated with the test substance Isophorone diisocyanate (IPDI) at the 4 mg/m3 exposure level showed signs of maternal toxicity (respiratory tract affected, decrased respiratory rate (bradypnea), laboured breathing, breathing sounds, reddish encrusted nostrils, serous nasal discharge,
rough fur, decreased feed intake, body weight loss). The incidence and type of fetal malformations were unaffected by treatment at an exposure level up to and including 4 mg/m3. Even if a treatment related effect was taken into consideration, it would be considered secondary to maternal toxicity.
Thus under the conditions of this study the test substance Isophorone diisocanate is considered to be not teratogenic. All signs of developmental
toxicity observed at the 4 mg/m3 exposure level (i.e. reduced fetal weights, delayed descensus testis and slightly retarded ossification) were
indicative of delayed fetal development and were only seen in the presence of maternal toxicity and thus considered a secondary effect. Animals
treated with the test substance at the 4 mg/m3 exposure level showed signs of maternal toxicity (respiratory tract affected, decrased respiratory
rate (bradypnea), laboured breathing, breathing sounds, reddish encrusted nostrils, serous nasal discharge, rough fur, decreased feed intake, body weight loss). Summarizing and evaluating all data investigated the following no-observed-adverse-effect concentrations (NOAECs) were determined: Maternal toxicity: 1 mg/m3
Developmental toxicity: 1 mg/m3 - Executive summary:
Female inseminated Wistar rats were treated daily for 6 hours/day by inhalation (nose-only) with Isophorone diisocyanate (IPDI) from day 6 to day 19 post coitum to examine potential developmental toxicity effects of the test substance. Dosages used were 0 (air control); 0.25; 1 and 4 mg/m3, respectively.
Animals treated with the test substance Isophorone diisocyanate (IPDI) at the 4 mg/m3 exposure level showed signs of maternal toxicity (respiratory tract affected, decrased respiratory rate (bradypnea), laboured breathing, breathing sounds, reddish encrusted nostrils, serous nasal discharge, rough fur, decreased feed intake, body weight loss). No mortalities were reported. Necropsy revealed no treatment releated gross pathological findings at an exposure level up to and including 4 mg/m3. With respect to the parameters of intrauterine development, gestation rate, postimplantation loss, mean litter size, fetal sex distribution and placental appearance were not affected by treatment with the test substance at an exposure level up to and including 4 mg/m3. Reduction of fetal weight was evident in the 4 mg/m3 group and treatment relationship could not be completely excluded for marginally impaired placental weight at the 4 mg/m3 exposure level.
The incidence and type of fetal malformations were unaffected by treatment at an exposure level up to and including 4 mg/m3. Slightly retarded ossification of few localizations (phalanges, sternebrae, sacral and caudal vertebrae) was assumed and slightly impaired descensus testis could not be completely excluded at the 4 mg/m3 exposure level in relation to decreased fetal weights and dose dependency. All signs of developmental toxicity observed at the 4 mg/m3 exposure level (i.e. reduced fetal weights, delayed descensus testis and slightly retarded ossification) were indicative of delayed fetal development and were only seen in the presence of maternal toxicity and thus considered a secondary effect. Summarizing and evaluating all data investigated the following no-observed-adverse-effect concentrations (NOAECs) were determined: Maternal toxicity: 1 mg/m3Developmental toxicity: 1 mg/m3
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