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EC number: 230-391-5 | CAS number: 7085-85-0
- 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

Carcinogenicity
Administrative data
- Endpoint:
- carcinogenicity
- Remarks:
- implantation
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Acceptable, well-documented publication which meets basic scientific principles
Data source
Reference
- Reference Type:
- publication
- Title:
- Long-Term Study of Aerosol Cyanoacrylate tissue Adhesive Spray: Carcinogenicity and Other Untoward Effects
- Author:
- Matsumoto et. al.
- Year:
- 1 969
- Bibliographic source:
- The American Surgeon, Novenber, 1969, Vol 35, No 11, 825-827
- Report date:
- 1969
Materials and methods
Test guideline
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- In dogs, a wound was created in the liver, kidney, femoral artery or small bowel. Hemostasis or anastomosis was accomplished by cyanoacrylate monomer spray using nitrogen or Freon as a propellant.
In rats and mice, under general anesthesia a 3 cm incision was made at the upper abdomen, and the peritoneum was entered. In some animals 0.5 cc. of cyanoacrylate monomer was sprayed into the abdominal cavity on the surface of the liver. - GLP compliance:
- no
Test material
- Reference substance name:
- n-butyl cyanoacrylate
- IUPAC Name:
- n-butyl cyanoacrylate
- Reference substance name:
- isobutyl cyanoacrylate
- IUPAC Name:
- isobutyl cyanoacrylate
Constituent 1
Constituent 2
Test animals
- Species:
- dog
- Strain:
- other: mongrel
- Sex:
- not specified
- Details on test animals or test system and environmental conditions:
- weight of the dogs: 11 to 28 kg
They also used rats:
Strain: Walter Reed
Weight: 180 -210 g
Age: 10 months
And they used mice:
Strain Wlater Reed
Weight: 19-20 g
Age: 10 months
Administration / exposure
- Route of administration:
- implantation
- Vehicle:
- other: nitrogen and freon
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- single exposure
- Post exposure period:
- All animals were examined and autopsied when they died.
20 dogs were sacrified and auotopsied at 12 to 18 months.
All rats of the first generation were sacrified and autopsied at hte end of one year.
All mice were autopsied at the end of 12 months.
Doses / concentrations
- Remarks:
- Doses / Concentrations:
0.5 ml
Basis:
other: implanted
- No. of animals per sex per dose:
- 50 dogs per dose, 100 rats per dose, 100 mice per dose
- Details on study design:
- In dogs, a wound was created in the liver, kidney, femoral artery or small bowel. Hemostasis or anastomosis was accomplished by cyanoacrylate monomer spray using nitrogen or Freon as a propellant.
In the rat, under general anesthesia with ether the abdomen was prepared with merthiolate. A 3 cm incision was made at the upper abdomen, and the peritoneum was entered. In some animals 0.5 cc. of cyanoacrylate monomer was sprayed into the abdominal cavity on the surface of the liver using nitrogen spray gun or by means of aerosol spray. The abdominal wound was closed with metal clips. Essentially the same procedures were followed in mice.
The animals were divided into three groups:
Group I = 50 dogs
Group II = 100 rats
Group III = 100 mice
Group I was further diveded into 3 subgroups according to the monomer used:
Subgroub 1 = n-butyl cyanoacrylate with spray gun (20 dogs)
Subgroup 2 = isobutyl cyanoacrylate with spray gun (20 dogs)
Subgroup 3 = aerosol n-butyl spray (10 dogs)
Each of Group II and III further divided into seven subgroups:
Subgroup 1 = n-butyl cyanoacrylate with spray gun ( 10 animals)
subgroup 2 = isobutyl cyanoacrylate with spray gun (10 animals)
Subgroup 3 = aerosol n-butyl spray (20 animals)
Subgroup 4 = aerosol isobutyl spray (20 animals)
Subgroup 5 = Freon (10 animals)
Subgroup 6 = Freon 114 (10 animals)
Subgroup 7 = Mixture of Freon 12 and 114 (20 animals)
At six months after surgery 16 pairs of male and female rats in subgroup 3 and 4 were kept in 16 individual cages and 5 rats of second generation born to each of 16 pairs (total of 80 rats) were kept and observed for possible abnormal development.
Examinations
- Observations and examinations performed and frequency:
- All animals were routinely examined and autopsied when they died. Twenty dogs were sacrifired and auutopsied at 12 to 18 months. All rats of the first generation were sacrified and autopsied at the end of one year after surgery and abdominal cavity was examined. A piece of liver was obtained for microscopic study.
Half of the total number of rats in the second generation were autopsied and the same examiantions were performed at 6 months.
All mice were autopsied at the end of 12 months after surgery. - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
Results and discussion
Results of examinations
- Details on results:
- Dogs:
In the 50 dogs studied, three were eliminated from the study in the acute phase. At autopsy, gross and microscopy findings were similar at each site of adhesive application. Adhesives, often very dense, were noted. On the surface of the organs, particulary the liver or the kidney, polymer fragments were seen. some polymer had been extruded from the depths of the organs. In blood vessels and kidney specimens, some material was occasionally seen in the lumens. On microscopic examination small particles of polymer, 10 to 50 u, were seen implanted in the tissue. These particles were surrounded by a granulomatous reaction with giant cells. No changes suggestive of neoplasm were seen. No tumor foramtion or mitotic change of cells was noted in any of the animals. 27 dogs are being kept for a longer period.
Rats:
Six rats in the first generation died in 10 to 12 months after surgery. These rats appeared to be very old and senile. Four rats died with pneumonia and two died without pathological findings.
No death was noted and no evidence of tumor formation was found due to the monomer or Freon in all rats sacrified at the age of 22 months.
No pathologic development was found in 80 rats of the second generation.
Mice:
No mice died spontanously. Autopsy finding of these animals and others sacrified one year after surgery revealed no evidence of tumor formation exept scattered adhesions of omentum and liver in which easily removable small amounts of polymer fragments were seen.
Microscopic findings of examined liver revealed no pathologic findings.
- Relevance of carcinogenic effects / potential:
- The test substances have no carcinogenic potential.
Effect levels
open allclose all
- Dose descriptor:
- NOAEC
- Remarks on result:
- not determinable
- Remarks:
- no NOAEC identified
- Dose descriptor:
- NOAEL
- Remarks on result:
- not determinable
- Remarks:
- no NOAEL identified
- Dose descriptor:
- T25
- Remarks on result:
- not determinable
- Remarks:
- no T25 identified
Applicant's summary and conclusion
- Conclusions:
- In this study n-butyl cyanoacrylate and isobutyl cyanoacrylate were tested.
No tumor formation, either gross or microscopic, was seen in a series of dogs studied up to 2 years.
Similar results were found in rats and mice, as well as in the following generation of rats born to treated animals.
27 dogs still alive showed no symptoms or evidence of tumor formation at that time. - Executive summary:
Aim of study
The aim of this study was to investigate possible carcinogenic effects by the test substances following a implantation.
Administration of the test substance
In dogs, a wound was created in the liver, kidney, femoral artery or small bowel. Hemostasis or anastomosis was accomplished by cyanoacrylate monomer spray using nitrogen or Freon as a propellant. In rats and mice, under general anesthesia a 3 cm incision was made at the upper abdomen, and the peritoneum was entered. In some animals 0.5 cc. of cyanoacrylate monomer was sprayed into the abdominal cavity on the surface of the liver.
Investigations:
The animals were investigated up to 2 years.
Results
No tumor formation, either gross or microscopic, was seen in a series of dogs studied up to 2 years. Similar results were found in rats and mice, as well as in the following generation of rats born to treated animals. 27 dogs still alive show no symptoms or evidence of tumor formation at that time.
The test substances n-butyl cyanoacrylate and isobutyl cyanoacrylate showed no carcinogenic potential.
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