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Diss Factsheets
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EC number: 907-605-7 | CAS number: 68815-47-4
- 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
Basic toxicokinetics
Administrative data
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Study period:
- No data
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Only short study summary available (lots of data missing: number of animals, precise dose administered, precise data (mean ± SD) on urine analysis, data on test material (purity...), metabolites not fully identified).
Cross-reference
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 1 983
Materials and methods
- Objective of study:
- distribution
- excretion
- metabolism
- Principles of method if other than guideline:
- Analysis of distribution of radiolabelled test material by radioactivity quantification in selected organs after a single oral administration (after 72 h).
Analysis of distribution of radiolabelled test material by autoradiography after a single intravenous injection (after 1 h and 24 h).
Analysis of urine metabolites after a single oral administration or radiolabelled test material. - GLP compliance:
- not specified
Test material
- Reference substance name:
- Hexamethylenediammonium dichloride
- EC Number:
- 227-977-8
- EC Name:
- Hexamethylenediammonium dichloride
- Cas Number:
- 6055-52-3
- IUPAC Name:
- hexane-1,6-diamine dihydrochloride
- Details on test material:
- - Name of test material (as cited in study report): 1,6-diaminohexane; hexamethylenediamine; 1,6-hexamethylenediamine-1,6-[14C]dihydrochloride (radiolabelled substrance)
- Specific activity: 30 mCi/mmol
- Source: Midwest Research Institute (Kansas City, MO)
Constituent 1
- Radiolabelling:
- yes
- Remarks:
- 14C
Test animals
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River, Kingston, NY
- Weight at study initiation: 200-250 g
- Housing: hanging wire cages
- Individual metabolism cages: yes
- Diet (e.g. ad libitum): NIH-07 rodent diet (Zeigler Bros., Gardners, PA), ad libitum
- Water (e.g. ad libitum): tap water, ad libitum
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 21 ± 1 °C
- Humidity (%): 50
- Photoperiod (hrs dark / hrs light): 12/12
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- water
- Details on exposure:
- No data
- Duration and frequency of treatment / exposure:
- single dose
Doses / concentrations
- Remarks:
- Doses / Concentrations:
Experiment 1: 0.4 mg/kg corresponding to 25 µCi/250 g body weight (oral administration)
Experiment 2: 100 µCi/animal (intravenous injection)
Experiment 3: 100-200 µCi
- No. of animals per sex per dose / concentration:
- Experiment 1: 4 males for oral exposure
Experiment 2: 2 males and 2 females for intravenous injection
Experiment 3: male rats, No. not specified - Control animals:
- no
- Positive control reference chemical:
- No
- Details on study design:
- No data
- Details on dosing and sampling:
- + Oral exposure:
- Dispositions testing - the animals were placed in metabolism cages, and excreta, including expired air, were collected for 72 h. Then, the animals were killed and selected tissues, as well as the carcass, were analyzed for residual radioactivity (tissues were homogenized and after further treatment radioactivity was determined using a scintillation counter).
- Analysis of urine - urine was collected on dry ice for approx. 24 hours and analysed by HPLC and TLC. Samples were injected into a column, chromatography was run using a 45-65% methanol gradient containing 25ml/l PIC-B7 (Waters) over a 7 minute period. Fractions were collected every 0.2 minutes and counted in a scintillation counter. Urine samples were also spotted on TLC plates, after further processing radioactivity was determined using a TLC scanner.
+ Intravenous injection: Male and female rats were administered 100 µCi of test material, and one animal of each sex was killed at 1 h and at 24 h post-injection. Sections were prepared as described by Irons and Gross and analyzed by whole-body autoradiography (exposed for either 1 week (1-h animals) or for 10 days (24-h animals)). - Statistics:
- None
Results and discussion
- Preliminary studies:
- No data
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- no data
- Details on distribution in tissues:
- The prostate contained the highest concentration of radioactivity 72 h after oral administration (table 1). Whole-body autoradiography showed that 1 h after injection, the intestine contained the greatest amount of radioactivity in a male rat followed by liver and kidney. The prostate gland was well below the liver in intensity of radiolabel. There was little radioactivity in the brain or testes. At 24 h post injection, the prostate gland contained the greatest concentration of radioactivity followed by intestine and liver. Thus, radiolabelled material either accumulates slowly in the prostate or persists in that gland for a relatively long time.
The uterus of the female rat was found to have a high concentration of radiolabel 1 h after injection but not 24 h afterwards. The accumulation of radiolabel in the uterus may be dependent on the estrous cycle. Little radioactivity was found in the ovary at either time period.
- Details on excretion:
- The principal route of elimination of radioactivity following oral administration was the urine (47% of the dose). About 20% of the administered radioactivity was excreted as C02 over a 72-h period while the feces contained 27%. Very little radioactivity was retained by the animals 72 h after treatment (<1.5%).
Metabolite characterisation studies
- Metabolites identified:
- yes
- Details on metabolites:
- Urine samples from treated animals were analyzed by HPLC and TLC and were observed to contain two major peaks of radioactivity. One of these, comprising 30% of the total radioactivity in the urine, comigrated with authentic 1,6-diaminohexane in both chromatographic systems.
Any other information on results incl. tables
Tissue distribution of residual radioactivity 72 h after oral administration of radiolabelled 1,6-diaminohexanedihydrochloride
Tissue or fluid |
Concentration of radiolabel (mean ± SD of 4 male rats in nmol equiv./g tissue or fluid) |
Prostate |
250 ± 30 |
Intestine |
113 ± 8 |
Kidney |
194 ± 27 |
Liver |
171 ± 26 |
Spleen |
82 ± 13 |
Testes |
64 ± 8 |
Lungs |
77 ± 11 |
Head |
51 ± 8 |
Brain |
25 ± 6 |
Blood |
31 ± 5 |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information): no bioaccumulation potential based on study results
Following oral administration of 1,6-Hexamethylenediamine-1,6-[14C]dihydrochloride to male Fischer-344 rats, about 20% of the administered dose was recovered as CO2 after 72 h. Urinary and fecal excretion accounted for 47% and 27% of the administered radioactivity, respectively. - Executive summary:
Following oral administration of 1,6-Hexamethylenediamine-1,6-[14C]dihydrochloride (HDDC) as salt of HMD, to male Fischer-344 rats, about 20% of the administered dose was recovered as CO2 after 72 h. Urinary and fecal excretion accounted for 47% and 27% of the administered radioactivity, respectively. Two peaks were found in urine with one of them, corresponding to 30 % of total radioactivity in urine and comigrating with 1,6-diaminohexane.
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