Registration Dossier
Registration Dossier
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: 200-471-4 | CAS number: 60-34-4
- 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 relevant data were available: a minimal effect on mouse sperm cells was noted, but:
- the dosing route (i.p.) was not relevant for a chemical
- effect was at most 4% abnormal cells at doses as high as 40% of the LD50 (12 mg/kg, i.p.)
- there was no impact on total sperm cell number, testes weight, testes histopathology
- as animals were not paired, relevance towards fertility is unknown
Link to relevant study records
- Endpoint:
- toxicity to reproduction
- Remarks:
- other: effects on sperm cells
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Non guideline study, prior to GLP, unknown relevance for fertility assessment in absence of pairing. General pathology and hematology data were ignored as it was unclear in which study design and with which test item these investigations were done.
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Examination of sperm parameters after repeated exposure by inhalation
- GLP compliance:
- no
- Remarks:
- prior to GLP
- Species:
- mouse
- Strain:
- B6C3F1
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- age from 11 to 18 weeks,
caged in groups of 3 to 5 animals each in plastic cages
air conditioned rooms
automated light-dark cycles (10:14 hours)
food and water ad libitum - Route of administration:
- intraperitoneal
- Vehicle:
- water
- Remarks:
- distilled
- Details on mating procedure:
- not performed
- Analytical verification of doses or concentrations:
- no
- Duration of treatment / exposure:
- dose prepared <0.5 h before injection
- Frequency of treatment:
- 5 injections
- Details on study schedule:
- Study 1): time-dependency: Five animals of each group were sacrificed by cervica! dislocation at weekly intervals.
Study 2): dose-dependency: 0.8 and 3 weeks after exposure - Remarks:
- Doses / Concentrations:
3 mg/kg
Basis:
other: nominal injected - No. of animals per sex per dose:
- Study 1): 50 males at 3 mg/kg
Study 2): 2 or 3 males at 7.5 or 12 mg/kg - Control animals:
- yes, concurrent vehicle
- Parental animals: Observations and examinations:
- Study 1): body weights recorded
- Sperm parameters (parental animals):
- Study 1): number and percent of abnormally shaped sperm-per cauda epididymis were scored
Study 2): abnormally shaped sperm in the cauda epididymis 3.5 weeks after injection
The average of 1000 to 2000 sperm were analyzed on two separate air-dried smears prepared from a pooled suspension of the sperm from the cauda epididymides of two or three mice. All countings of the sperm were conducted as blind experiments. - Postmortem examinations (parental animals):
- Study 1): ratios of testis to body weight, histopathology of the testes (PAS-hematoxylin)
- Clinical signs:
- not examined
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- effects observed, treatment-related
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Histopathological findings: non-neoplastic:
- no effects observed
- Description (incidence and severity):
- testes
- Other effects:
- not examined
- Reproductive function: oestrous cycle:
- not examined
- Reproductive function: sperm measures:
- effects observed, treatment-related
- Reproductive performance:
- not examined
- Dose descriptor:
- LOAEL
- Effect level:
- 12 mg/kg bw/day
- Sex:
- male
- Basis for effect level:
- reproductive function (sperm measures)
- Clinical signs:
- not examined
- Mortality / viability:
- not examined
- Body weight and weight changes:
- not examined
- Sexual maturation:
- not examined
- Organ weight findings including organ / body weight ratios:
- not examined
- Gross pathological findings:
- not examined
- Histopathological findings:
- not examined
- Remarks on result:
- not measured/tested
- Reproductive effects observed:
- not specified
- Executive summary:
MMH has the ability to increase sperm malformation, however this effect is minimal:
- at most 4% abnormal cells at doses as high as 40% of the LD50 (12 mg/kg, i.p.)
- no impact on total sperm cell number, testes weight, testes histopathology
The fertility was not assessed in this study (no pairing of animals).
Reference
Study 1): decreased until 5 weeks after exposure; weight gain unaffected after exposure
Sperm:
Study 1): maximum effect of more than doubling the background incidence of abnormal sperm shape (i.e.: at most 4% in treated animals), between 1 and 3 weeks after the end of exposure. Reversible in 7 weeks. No clear effect on sperm count.
Study 2): same effects, dose-dependent: > doubling (<4% abnormal) at 12 mg/kg, < doubling (<3% abnormal) at 7.5 mg/kg.
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
All data that might suggest an embryotoxic or teratogenic effect were obtained with doses producing significant/marked maternal toxicity (marked decrease in bodyweight gain at the 2 higher doses and convulsions at the highest dose).
Link to relevant study records
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Deviations:
- yes
- Remarks:
- intraperitoneal route of administration, treatment during days 6-15 of gestation, less than 20 females/group
- GLP compliance:
- no
- Limit test:
- no
- Specific details on test material used for the study:
- Provider: Eastman, Rochester, N.Y.
- Species:
- rat
- Strain:
- Fischer 344
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Breeding Laboratories, Wilmington, Mass
- Housing: 3 per plastic cages containing woodchip bedding
- Diet (e.g. ad libitum): pelleted feed (Ralston Purina Co., St. Louis, Mo.), ad libitum
- Water (e.g. ad libitum): ad libitum
ENVIRONMENTAL CONDITIONS
- Temperature : 72 ± 2°F
- Photoperiod (hrs dark / hrs light): 12-h light/dark cycle - Route of administration:
- intraperitoneal
- Vehicle:
- physiological saline
- Details on exposure:
- All dose volumes were 2 mL/kg. Solutions were prepared daily in physiologic saline.
- Analytical verification of doses or concentrations:
- no
- Details on mating procedure:
- Two females were placed overnight with each male and checked for presence of sperm by vaginal wash the next morning. The day on which sperm was detected was considered d 0 of pregnancy.
- Duration of treatment / exposure:
- Days 6-15 of gestation
- Frequency of treatment:
- daily
- Dose / conc.:
- 2.5 mg/kg bw/day (nominal)
- Dose / conc.:
- 5 mg/kg bw/day (nominal)
- Dose / conc.:
- 10 mg/kg bw/day (nominal)
- No. of animals per sex per dose:
- 13 to 16
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: Appropriate dose ranges for the three compounds were established during preliminary studies using groups of three or four pregnant animals. Parameters of toxicity observed in the higher dose preliminary treatment groups were maternal mortality and weight loss or markedly reduced weight gains and or convulsions (ranging from moderate to severe/resulting in mortality)
- The pregnant rats were sacrificed on gestation day 20 by overdose of halothane - Maternal examinations:
- The pregnant rats were weighed daily.
- Ovaries and uterine content:
- The uterus was opened and the numbers and positions of implants, dead fetuses, live fetuses, and resorptions were recorded
- Fetal examinations:
- Live fetuses were blotted dry, weighed, examined for external abnormalities, and divided into groups for visceral and skeletal examination (two-thirds and one-third of each litter, respectively). Fetuses for visceral examination were fixed in Bouin solution for at least 2 wk and were then examined by the freehand razor sectioning technique of Wilson (1965). The remaining fetuses were processed by an Alizarin red staining technique for skeletal examination (Dawson, 1926).
- Statistics:
- Maternal and fetal body weights and numbers of implants and resorptions were analyzed by the Student's t-test and are listed as mean ± standard deviation. Incidence of abnormalities was analyzed with Fisher's exact test. The litter was used as the experimental unit for those data that could be analyzed using either litter or fetus as the experimental unit, and a probability of p<0.05 was accepted as significant in all analyses.
- Clinical signs:
- effects observed, treatment-related
- Description (incidence and severity):
- Four of the pregnant females in the high-level treatment group convulsed following methylhydrazine injection on one or more occasions during the treatment period.
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Maternal weight gains were significantly less in all treatment groups during the early (days 6-10) part of the treatment period and significantly less for the two higher treatment groups during the latter (days 11-16) part of the treatment period (See Table 1). Significant decreases in weight gains for treatment groups were not seen after cessation (days 17-20) of treatment; however, overall weight gains were lower than those of the control group (-14%, -29% and -41% of controls in the 2.5, 5 and 10 mg/kg bw/day groups, respectively).
- 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 examined
- Neuropathological findings:
- not examined
- Histopathological findings: non-neoplastic:
- not examined
- Histopathological findings: neoplastic:
- not examined
- Other effects:
- not examined
- Number of abortions:
- no effects observed
- Pre- and post-implantation loss:
- no effects observed
- Total litter losses by resorption:
- no effects observed
- Early or late resorptions:
- effects observed, treatment-related
- Description (incidence and severity):
- High incidence of resorptions in the two higher dose groups
- Dead fetuses:
- no effects observed
- Changes in pregnancy duration:
- not examined
- Changes in number of pregnant:
- no effects observed
- Other effects:
- not examined
- Dose descriptor:
- NOAEL
- Effect level:
- 2.5 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Basis for effect level:
- body weight and weight gain
- clinical signs
- early or late resorptions
- Abnormalities:
- not examined
- Fetal body weight changes:
- not examined
- Reduction in number of live offspring:
- no effects observed
- Changes in sex ratio:
- not examined
- Changes in litter size and weights:
- no effects observed
- Changes in postnatal survival:
- not examined
- External malformations:
- effects observed, non-treatment-related
- Description (incidence and severity):
- Intermediate dose group had a moderate increase in abnormalities involving the eyes (anophthalmia and/or microophthalmia) but the higher dose group had only a slight increase in abnormalities involving the eye
- Skeletal malformations:
- no effects observed
- Visceral malformations:
- no effects observed
- Other effects:
- not examined
- Dose descriptor:
- NOAEL
- Effect level:
- 2.5 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- external malformations
- Abnormalities:
- effects observed, non-treatment-related
- Localisation:
- external: eye
- Description (incidence and severity):
- Intermediate dose group had a moderate increase in abnormalities involving the eyes (anophthalmia and/or microophthalmia) but the higher dose group had only a slight increase in abnormalities involving the eye
- Developmental effects observed:
- no
- Conclusions:
- All data that might suggest an embryotoxic or teratogenic effect were obtained with doses producing significant/marked maternal toxicity (marked decrease in bodyweight gain at the 2 higher doses and convulsions at the highest dose)
- Executive summary:
Pregnant Fischer female rats were treated daily with methylhydrazine intraperitoneal injections during gestation Days 6 -15 at 2.5, 5 and 10 mg/kg bw/day. The pregnant rats were weighed daily. The uterus was opened and the numbers and positions of implants, dead fetuses, live fetuses, and resorptions were recorded. Live fetuses were blotted dry, weighed, examined for external abnormalities, and divided into groups for visceral and skeletal examination (two-thirds and one-third of each litter, respectively).
Four of the pregnant females in the high-level treatment group convulsed following methylhydrazine injection on one or more occasions during the treatment period. Maternal weight gains were significantly less in all treatment groups during the early (days 6-10) part of the treatment period and significantly less for the two higher treatment groups during the latter (days 11-16) part of the treatment period (See Table 1). Significant decreases in weight gains for treatment groups were not seen after cessation (days 17-20) of treatment; however, overall weight gains were lower than those of the control group (-14%, -29% and -41% of controls in the 2.5, 5 and 10 mg/kg bw/day groups, respectively). High incidence of resorptions in the two higher dose groups was observed. Intermediate dose group had a moderate increase in abnormalities involving the eyes (anophthalmia and/or microophthalmia) but the higher dose group had only a slight increase in abnormalities involving the eye.
All data that might suggest an embryotoxic or teratogenic effect were obtained with doses producing significant/marked maternal toxicity (marked decrease in bodyweight gain at the 2 higher doses and convulsions at the highest dose). Therefore NOAEL for maternal toxicity and developmental toxicity were both identified at 2.5 mg/kg bw/day.
Reference
Table 1: Effects of methylhydrazine given intraperitoneally on days 6 -15 of gestation in the rat
|
Methylhydrazine dose (mg/kg bw/day) |
|||
Effect |
0 (13 litters) |
2.5 (15 litters) |
5 (15 litters) |
10 (16 litters) |
Gestation weight gain of females (g)a |
|
|
|
|
Days 6-10 |
8 ± 5 |
3 ± 3b |
2 ± 4b |
- 3 ± 3b |
Days 11-16 |
21 ± 5 |
19 ± 10 |
15 ± 5b |
12 ± 8b |
Days 17-20 |
30 ± 6 |
29 ± 10 |
25 ± 10 |
26 ± 12 |
Litter data |
|
|
|
|
Implants/littera |
7.8 ± 3.6 |
8.8 ± 3.4 |
7.3 ± 2.5 |
7.6 ± 3.4 |
Viable fetuses/littera |
6.8 ± 4.0 |
7.5 ± 3.4 |
6.2 ± 2.7 |
6.1 ± 3.9 |
Fetal weighta |
3.1 ± 0.3 |
3.3 ± 0.3 |
3.1 ± 0.3 |
3.2 ± 0.3 |
Litters with ≥ 33% fetuses resorbed |
0 |
2 |
3 |
3 |
Incidence of abnormalities: |
|
|
|
|
Litters (fetuses) affected |
|
|
|
|
Gross examc |
2(2) |
1(1) |
3(4) |
2(2) |
Soft-tissue exam |
1(1)d |
2(2)e |
6(9)e |
3(4)f |
Skeletal examg |
0(0) |
1(1) |
1(1) |
2(2) |
aMean ± standard deviation.
bSignificant at ≤ 0.05 level.
cAII nanoids (≤ control mean fetal weight minus 3 standard deviations).
dOne fetus with anophthalmia and hydrocephalus.
eAII anophthalmia or severe microophthalmia.
fHydronephrosis and dilated ureter in 1 fetus, hydrocephalus in another, and 2 fetuses with anophthalmia.
gAll unfused ossification centers of vertebrae.
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- no study available
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
Pregnant Fischer female rats were treated daily with methylhydrazine intraperitoneal injections during gestation Days 6 -15 at 2.5, 5 and 10 mg/kg bw/day. The pregnant rats were weighed daily. The uterus was opened and the numbers and positions of implants, dead fetuses, live fetuses, and resorptions were recorded. Live fetuses were blotted dry, weighed, examined for external abnormalities, and divided into groups for visceral and skeletal examination (two-thirds and one-third of each litter, respectively).
Four of the pregnant females in the high-level treatment group convulsed following methylhydrazine injection on one or more occasions during the treatment period. Maternal weight gains were significantly less in all treatment groups during the early (days 6-10) part of the treatment period and significantly less for the two higher treatment groups during the latter (days 11-16) part of the treatment period (See Table 1). Significant decreases in weight gains for treatment groups were not seen after cessation (days 17-20) of treatment; however, overall weight gains were lower than those of the control group (-14%, -29% and -41% of controls in the 2.5, 5 and 10 mg/kg bw/day groups, respectively). High incidence of resorptions in the two higher dose groups was observed. Intermediate dose group had a moderate increase in abnormalities involving the eyes (anophthalmia and/or microophthalmia) but the higher dose group had only a slight increase in abnormalities involving the eye.
All data that might suggest an embryotoxic or teratogenic effect were obtained with doses producing significant/marked maternal toxicity (marked decrease in bodyweight gain at the 2 higher doses and convulsions at the highest dose). Therefore NOAEL for maternal toxicity and developmental toxicity were both identified at 2.5 mg/kg bw/day.
Justification for classification or non-classification
Additional information
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.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.