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EC number: 231-635-3 | CAS number: 7664-41-7
- 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Published paper; investigative study
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Localized and systemic effects of environmental ammonia in rats
- Author:
- Schaerdel, A.D., White, W.J., Lang, C.M., Dvorchik, B.H. and Bohner, K.
- Year:
- 1 983
- Bibliographic source:
- Lab Anim Sci; 33 (1), 1983, 40-45.
Materials and methods
- Objective of study:
- absorption
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 417 (Toxicokinetics)
- Principles of method if other than guideline:
- Rats with surgically implanted aortic cannulas were exposed to varying environmental ammonia concentrations (15-1157 ppm). Blood pH, pCO2 (partial pressure of CO2), PO2 (partial pressure of O2) and blood ammonia concentration were measured.
- GLP compliance:
- not specified
Test material
- Reference substance name:
- Ammonia, anhydrous
- EC Number:
- 231-635-3
- EC Name:
- Ammonia, anhydrous
- Cas Number:
- 7664-41-7
- Molecular formula:
- H3N
- IUPAC Name:
- ammonia
- Details on test material:
- No further information
Constituent 1
- Radiolabelling:
- no
Test animals
- Species:
- rat
- Strain:
- other: Crl:COBS CD(SD)
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- The animals were male Crl:COBS CD(SD) rats weighing 300 to 400 g, obtained from Charles River Laboratories (MA). The rats were quarantined for 5 days, in groups of 6 in stainless steel wire-bottom suspended cages. The quarantine cubicles had an environmental temperature of 21±0.5°C, 50±20% relative humidity, 29 fresh air changes per hour, and a 12-hour light/dark photoperiod.
The rats received a commercial rodent diet (RMH 3000) and water ad libitum. Urine and faeces were removed from the cages daily to reduce endogenous production of ammonia and other gaseous contaminants. No ammonia was detected in the quarantine cubicles throughout the course of the study.
Administration / exposure
- Route of administration:
- inhalation
- Vehicle:
- unchanged (no vehicle)
- Details on exposure:
- The ammonia exposure was conducted in a clear rigid plastic isolator fitted with two sets of rubber gloves. The atmosphere inside the chamber was produced by mixing compressed air and anhydrous ammonia. The total gas flow, measured at the outflow port of the chamber with a thermal anemometer, was set to 35 litres/minute (providing 3 complete air changes per hour).
The ammonia concentration within the chamber was measured for each exposure group by the gas impingement technique. Daily measurements of ammonia concentration, temperature and relative humidity inside the chamber were made during each exposure period. - Duration and frequency of treatment / exposure:
- Phase 1: single exposure of 24 hours
Phase 2: 3 or 7 day continuous exposure
Doses / concentrations
- Remarks:
- Doses / Concentrations:
The rats were exposed to varying environmental ammonia concentrations (15-1157 ppm).
- No. of animals per sex per dose / concentration:
- Phase 1: 3 males/dose
Phase 2: 14 males/dose, divided into two subgroups of 7/dose - Control animals:
- yes, concurrent vehicle
- Positive control reference chemical:
- A positive control was not included.
- Details on study design:
- The purpose of the study was to determine if environmental ammonia was absorbed through the lungs of the rats into the blood and exerted an effect on blood pH, blood gases and hepatic drug metabolizing enzyme activity. In phase 1 of the study, rats were exposed to varying environmental ammonia concentrations (15-1157 ppm). Blood pH, pCO2, pO2 and blood ammonia concentrations were measured at 0, 8, 12 and 24 h post exposure. In phase 2, hepatic microsomal enzyme activity (ethylmorphine-N-demethylase and cytochrome P-450) was determined after a 3 or 7 day exposure to varying environmental ammonia concentrations (4-714 ppm).
- Details on dosing and sampling:
- In phase 1 of the study, rats were exposed to varying environmental ammonia concentrations (15-1157 ppm). Blood pH, pCO2, pO2 and blood ammonia concentrations were measured at 0, 8, 12 and 24 h post exposure. In phase 2, hepatic microsomal enzyme activity (ethylmorphine-N-demethylase and cytochrome P-450) was determined after a 3 and 7 day exposure to varying environmental ammonia concentrations (4-714 ppm).
All arterial blood samples were collected through a permanently implanted aortic cannula (fitted under general anaesthesia). The animals were placed in individual metabolism cages within the chamber. Blood samples were collected by connecting a 3 ml heparinised syringe to the adaptor needle on the cannula and withdrawing 1 ml of blood. Blood gas and pH determinations were done on 0.6 ml samples of blood, using a pH/blood gas analyser. Blood ammonia concentrations were measured on 0.3 ml samples using the glutamate dehydrogenase procedure.
On the 3rd and 7th days of exposure in phase 2, one subgroup was removed from the isolator, and the animals decapitated. The liver microsomal fraction was isolated from the right lateral and left liver lobes, frozen in liquid nitrogen, and stored at -70°C. At the time of analysis, the final protein concentration of the microsomal fraction was adjusted to 0.75 mg of microsomal proten per ml of solution.
The trachea and lungs were also removed following phase 2 exposure and perfused with 10% neutral buffered formalin for 1 week. Sections were prepared, then embedded and stained with haematoxylin and eosin for histological examination. - Statistics:
- Two way ANOVA with repeated measures of one factor was applied to phase 1 data. A three way factorial analysis was used to analyse phase 2 data. Comparisons were made using the Newman-Keul technique. In phase 2, significant differences between daily values were determined by the orthogonal components technique. A linear regression was done on each time period in phase 1.
Results and discussion
- Preliminary studies:
- No preliminary studies conducted.
Toxicokinetic / pharmacokinetic studies
- Details on absorption:
- No significant changes were found in the blood pH and pCO2. The pO2 and the microsomal enzymes had only minor changes. The blood ammonia concentration increased significantly in a linear fashion with increasing environmental ammonia concentrations indicating pulmonary absorption of ammonia.
- Details on distribution in tissues:
- No changes in the histologic appearance of the lungs or trachea.
- Details on excretion:
- No parameter measured.
Metabolite characterisation studies
- Metabolites identified:
- not measured
- Details on metabolites:
- No further information
Any other information on results incl. tables
No significant changes were found in the blood pH and pCO2. The pO2 and the microsomal enzymes had only minor changes. The blood ammonia concentration increased significantly in a linear fashion with increasing environmental ammonia concentrations indicating pulmonary absorption of ammonia. These levels also declined over time at higher concentrations suggesting that compensation occurred. There was no evidence of toxicity of ammonia during the exposure periods.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results: no bioaccumulation potential based on study results
No significant changes were found in the blood pH and pCO2. The pO2 and the microsomal enzymes had only minor changes. The blood ammonia concentration increased significantly in a linear fashion with increasing environmental ammonia concentrations indicating pulmonary absorption of ammonia. - Executive summary:
The purpose of the study was to determine if environmental ammonia was absorbed through the lungs of the rats into the blood and exerted an effect on blood pH, blood gases and hepatic drug metabolizing enzyme activity. In phase 1 of the study, rats were exposed to varying environmental ammonia concentrations (15-1157 ppm). Blood pH, pCO2, pO2 and blood ammonia concentrations were measured at 0, 8, 12 and 24 h post exposure. In phase 2, hepatic microsomal enzyme activity (ethylmorphine-N-demethylase and cytochrome P-450) was determined after a 3 and 7 day exposure to varying environmental ammonia concentrations (4-714 ppm). No significant changes were found in the blood pH and pCO2. The pO2 and the microsomal enzymes had only minor changes. The blood ammonia concentration increased significantly in a linear fashion with increasing environmental ammonia concentrations indicating pulmonary absorption of ammonia.
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