Miljöpåverkan
Dexametason
Miljörisk:
Risk för miljöpåverkan av dexametason kan inte uteslutas då det inte finns tillräckliga ekotoxikologiska data.
Nedbrytning:
Dexametason är potentiellt persistent.
Bioackumulering:
Dexametason har låg potential att bioackumuleras.
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Detaljerad miljöinformation
Environmental Risk Classification
Predicted Environmental Concentration (PEC)
PEC is calculated according to the following formula:
PEC (μg/L) = (A*109*(100-R))/(365*P*V*D*100) = 1.37*10-6 * A * (100 - R) = 1.37*10-6 * 6.68 kg * 100 = 0.00091 μg/L = 0.91 ng/L
Where:
A = 6.6826 dexametasone (sum of 4.3866 kg dexametasone and 3.0198 kg dexametasone natriumphosphate, equaling 2.296 kg dexamethasone) (total sold amount API in Sweden year 2021, data from IQVIA).
R = 0 % removal rate (due to loss by adsorption to sludge particles, by volatilization, hydrolysis or biodegradation) = 0, if no data is available.
P = number of inhabitants in Sweden = 10 * 106
V (L/day) = volume of wastewater per capita and day = 200 (ECHA default) (ECHA 2008)
D = factor for dilution of waste water by surface water flow = 10 (ECHA default) (ECHA 2008)
Predicted No Effect Concentration (PNEC)
Ecotoxicological studies
Algae (Pseudokirchneriella subcapitata) (ISO 8692, 1987) (Della Greca et al. 2004):
ErC50 72 h (growth inhibition) > 100.0 mg/L
Crustacean (Daphnia magna):
Acute toxicity
EC50 24 h (immobilisation) > 100.0 mg/L (OECD 202) (Ciba-Geigy Project No. 830166)
Other ecotoxicity data:
Bacterial Respiration Inhibition:
EC50 3 h > 320 mg/L (Inhibition of Oxygen Consumption by activated sludge, 87/302/EEC, Part C) (ECOTOXICOLOGY Report N 139 05)
PNEC derivation:
No PNEC can be calculated since there is not sufficient information on environmental toxicity available
Environmental risk classification (PEC/PNEC ratio)
Calculation of a risk ratio is not possible, as there is not sufficient environmental toxicity data available. Therefore, the following phrase is used: "Risk of environmental impact of dexametasone cannot be excluded, since there is not sufficient ecotoxicity data available."
Degradation
Biotic degradation
Ready degradability:
0 %, not readily biodegradable (OECD301E) (Ciba-Geigy, Project No. 83 01 65)
Justification of chosen degradation phrase:
As dexamethasone does not fulfil the criteria for ready biodegradability, the following phrase is chosen for degradation potential: ‘Dexamethasone is potentially persistent.’
Bioaccumulation
Partitioning coefficient:
logKow = 1.83 (method unknown) (Alcon Technical Report No. 090:38560:0796)
Justification of chosen bioaccumulation phrase:
As log Kow < 4, the following statement is used for Dexamethasone: ‘Dexmethasone has low potential for bioaccumulation.’
Excretion (metabolism)
Dexamethasone is eliminated from plasma with a half-life of 2.4-3.5 hours. The mean plasma clearance is 245 mL/min.
Within 24 hours 64% of a radioactive dose of 0.5-1.5 mg dexamethasone is excreted in the urine. Up to 36% of the dose is recovered in the urine in the form of the principal metabolite, 6β-hydroxyldexamethasone, and about 2% of the dose is found in the form of unchanged dexamethasone (Millicorten® Basic Drug Information, CIBA, 1994).
References
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ECHA 2008, European Chemicals Agency. 2008 Guidance on information requirements and chemical safety assessment. http://guidance.echa.europa.eu/docs/guidance_document/information_requirements_en.htm
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Della Greca et al. 2004. Toxicity of prednisolone, dexamethason and their photochemical derivatives on aquatic organisms. Chemosphere 54, p. 629-637.
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Ciba-Geigy, Project No. 830166, Final report: 26.5.1983 (report / full reference not available)
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ECOTOXICOLOGY Report N 139 05 (report / full reference not available, including date)
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Ciba-Geigy, Project No. 83 01 65, Final report: 28.4.1983 (report / full reference not available)
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Alcon Technical Report No. 090:38560:0796 (report / full reference not available, including date)
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Millicorten® Basic Drug Information, CIBA, October 19th, 1994.
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Laboratories Limited, March 2009.