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EC number: 250-882-8 | CAS number: 31981-44-9
- 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
There is no fertility study conducted with gestonorone acetate (ZK 5624), read-across with studies with ZK 5623 (gestonorone caproate):
subcutaneous (Rat, females, non-GLP, Doses: 0/ 2/ 20/ 200 mg/kg, twice weekly, two weeks premating plus up to two weeks mating period): NOEL = 2 mg/kg (Poggel 1978)
subcutaneous (Rat, males, non-GLP, Doses: 0/ 2/ 20/ 60 mg/kg, twice weekly, 10 weeks premating plus up to two weeks mating period): NOEL = 2 mg/kg (Poggel 1979)
subcutaneous (Rat, males, non-GLP, Doses: 0/ 2/ 20/ 200 mg/kg, twice weekly, ten weeks premating plus up to two weeks during mating): NOEL = 2 mg/kg (Poggel 1978)
subcutaneous (Mouse-NMRI, non-GLP, Doses: 0/ appr. 12 mg/kg, Days 7 to 13 p.c.): NOEL > 12 mg/kg (Günzel 1968)
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
Additional information
There are no reproductive toxicity studies with ZK 5624 (gestonorone acetate). Results of studies conducted with a different ester of gestonorone (ZK 5623, gestonorone caproate) are regarded as representative as most likely ester cleavage occurs in vivo after administration.
Effects of gestonorone caproate (ZK 5623) on female fertiliy was assessed in rats with subcutaneous administration (twice weekly, two weeks premating and up to two weeks mating) of doses of 2, 20, and 200 mg/kg. Dose-dependently increased disturbance of fertility was seen at 20 mg/kg and higher. Reversibility of effects was shown in two subgroups at 20 and 200 mg/kg which were mated for up to six weeks after end of treatment. No effects on duration of pregnancy and embryofetal development was seen in pregnant animals. (Poggel 1978)
Effects of gestonorone caproate (ZK 5623) on male fertility was assessed in rats with subcutaneous administration (0/ 2/ 20/ 60 mg/kg, twice weekly, 10 weeks premating plus up to two weeks mating period). Male fertility was decreased dose dependently from 20 mg/kg onwards. Also a slight increase in resorption rate was observed. (Poggel 1979)
Effects of gestonorone caproate (ZK 5623) on male fertility was assessed in rats with subcutaneous administration (twice weekly, ten weeks premating and up to two weeks mating) of doses of 2, 20, and 200 mg/kg. Dose-dependently decreased male fertility was seen at the dose of 20 mg/kg and higher, including decreased weights of male reproductive organs. In addition, increased numbers of total resorptions were seen at 20 mg/kg and higher. However, results of a dominant lethal test in rats up to the highest tested dose of 60 mg/kg did not indicate a dominant-lethal effect of ZK 5623. (Poggel 1978)
In a study in mice, the effect of gestonorone caproate (ZK 5623) on embryofetal development including peri/ postnatal development of F1 generation and embryonic develoment of F2 generation was studied after subcutaneous administraton on Days 1, 7 and 14 p.c. at a dose of 0.3 mg/animal (appr. 12 mg/kg). There were no compound-related findings in this study. ZK 5623 was not teratogenic. (Günzel 1968)
The effects observed on male and female fertility are regarded as exaggerated pharmacodynamic effects as a consequence of the progestenic activity of ZK 5623.
Effects on developmental toxicity
Description of key information
There are no developmental toxicity studies
with gestonorone acetate (ZK 5624), read-across with studies with ZK
5623 (gestonorone caproate):
subcutaneous (Mouse-NMRI, non-GLP, Doses: 0/ appr. 12 mg/kg, Days 1, 7
and 14 p.c.): NOEL > 12 mg/kg (Günzel 1968)
subcutaneous (Rat, non-GLP, Doses: 0/ 2/ 20/ 200 mg/kg, Days 0 and 4
p.c.): NOEL = 200 mg/kg (Poggel 1978)
subcuatenous (Rat, non-GLP, Doses: 0/ 2/ 20/ 200/ 500, Days 7, 10, 13,
16 p.c.): NOEL (embryotoxicity) = 20 mg/kg; NOEL (maternotoxicity and
teratogenicity) > 500 mg/kg (Poggel 1978)
subcutaneous (Rabbit, non-GLP, Doses: 0/ 2/ 20/ 200 mg/kg, days 6, 9,
12, 15 p.c.): NOEL (embryotoxicity) = 20 mg/kg; NOEL (maternotoxicity
and teratogenicity) > 200 mg/kg (Poggel 1978)
subcutaneous (Rabbit, non-GLP, Doses: 0/ 20/ 200 mg/kg, days 6, 9, 12,
15 p.c.): NOEL (embryotoxicity) = 20 mg/kg; NOEL (maternotoxicity and
teratogenicity) > 200 mg/kg (Poggel 1979)
No teratogenic effects were observed in subcutaneous studies with gestonorone caproate.
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
There are no developmental toxicity studies with ZK 5624 (gestonorone acetate). Results of studies conducted with a different ester of gestonorone (ZK 5623, gestonorone caproate) are regarded as representative as most likely ester cleavage occurs in vivo after administration.
The effect of gestonorone caproate (ZK 5623) on embryofetal development was studied in mice with once daily subcutaneous administration from day 7 to 13 p.c. at a dose of 0.3 mg/animal (appr. 12 mg/kg). There were no compound-related findings in this study. ZK 5623 was not teratogenic. (Günzel 1968)
The effect of gestonorone caproate (ZK 5623) on early embryonic development was studied in rats after subcutaneous administration of doses of 0/ 2/ 20/ 200 mg/kg on Days 0 and 4 p.c. No effects on pregnancy and embryo-fetal development were seen in this study. (Poggel 1978)
The effect of gestonorone caproate (ZK 5623) on embryofetal development including peri-/postnatal development of F1 generation and embryonic development of F2 generation was studied in rats with subcutaneous administration of doses of 2, 20, 200 and 500 mg/kg on Days 7, 10, 13 and 16 p.c. At the dose of 200 mg/kg an higher, fetolethal effects were described due to prevention of spontaneous delivery. These findings are a consequence of the progestational activity of the ZK 5623. No compound-related findings were observed at lower doses in the dams, the F1 and the F2 generations. ZK 5623 was not teratogenic in this study. (Poggel 1978)
In rabbits, the effect of gestonorone caproate (ZK 5623) on embryofetal development was studied in two independent studies with subcutaneous administration of doses of 2, 20, and 200 mg/kg on Days 6, 9, 12 and 15 p.c. Results of both studies indicated retardational and embryolethal effects in the fetuses at the high dose of 200 mg/kg. No malformations were seen. ZK 5623 was not teratogenic in rabbits. (Poggel 1978, Poggel 1979)
Toxicity to reproduction: other studies
Description of key information
There is no reproductive toxicity study conducted with gestonorone acetate (ZK 5624), read-across with studies with ZK 5623 (gestonorone caproate):
subcutaneous (Rat, females, non-GLP, Doses: 0/ 2/ 20/ 200 mg/kg, Days 17 and 20 p.c.; Days 1, 4, 7, 10, 13, 16, 19 p.p.): NOEL = 20 mg/kg (Anonymous 1978)
Additional information
There are no reproductive toxicity studies with ZK 5624 (gestonorone acetate). Results of studies conducted with a different ester of gestonorone (ZK 5623, gestonorone caproate) are regarded as representative as most likely ester cleavage occurs in vivo after administration.
The effect of gestonorone caproate (ZK 5623) on peri- and postnatal development (effects on dams, reared pups of F1 generation and F2 fetuses) was assessed by subcutaneous treatment of rats (P generation) at end of pregnancy (Days 17 and 20 p.c.) and during the weaning period (Days 1, 4, 7, 10, 13, 16 and 19 p.p.) with doses of 2, 20 and 200 mg/kg. At the high dose, spontenous delivery was prevented by treatment in nearly all animals. Only dead fetuses were detected in high dose animals sacrificed on Day 24 p.c. No effects of ZK 5623 were seen on any of the other parameters assessed in this study at the two lower doses tested. (Anonymous 1978)
Effects on peri- and postnatal development were also assessed within embryofetal toxicity studies in mice and rats (see above). No effects were seen in mice at the high dose of 12 mg/kg. Prevention of spontaneous delivery and secondary fetolethality was the only effect in rats at high subcutaneous doses of 200 and 500 mg/kg.
Prevention of spontaneous delivery by ZK 5623 is a consequence of its progestational acitivity.
Justification for classification or non-classification
There are no experimental data on the reproductive toxicity of gestonorone acetate (ZK 5624) available. Corresponding to the progestogenic efficacy of the compound and based on experimental results with ZK 5623 (gestonorone caproate) the repeated exposure to pharmacologically active doses may result in disturbances of endogenous hormone production and consequently to reversible inhibition of fertility in men and women. No indication of a teratogenic potential even after partially embryolethal doses were observed during embryotoxicity studies with gestonorone caproate (ZK 5623) in mice, rats and rabbits. Furthermore, no adverse effects on the development of the offspring were recorded in peri/postnatal studies with gestonorone caproate in rats. Still as a precaution a risk of embryotoxic effects in humans should be taken into consideration if exposure to high loads of the drug occurs during pregnancy. In addition, it should be prudently assumed that the compound might be transferred into the milk of breast-feeding women and might lead to a disturbance of the development of the infant.
Based on the German legislation (TRGS-905) for gestagenes, gestonorone acetate is classified with category Repr. (F) Cat. 1A and Repr. (D) Cat. 1B according to Regulation (EC) 1272/2008 (CLP).
Additional information
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