Miljöpåverkan
Miljöinformationen för amiodaron är framtagen av företaget Sanofi AB för Cordarone®
Miljörisk:
Användning av amiodaron har bedömts medföra försumbar risk för miljöpåverkan.
Nedbrytning:
Amiodaron är potentiellt persistent.
Bioackumulering:
Amiodaron har hög 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)
PEC = 0.0529 µg/L
Where:
A = 384,9709 kg (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)
P = number of inhabitants in Sweden = 10*106
V (L/day) = volume of wastewater per capita and day = 200 (ECHA default) (Ref I).
D = factor of dilution of waste water by surface water flow = 10 (ECHA default) (Ref I).
Predicted No Effect Concentration (PNEC)
Ecotoxicological studies
Algae (Pseudokirchneriella subcapitata):
EC50 72 h (growth rate): >12 μg/L
NOEC 72 h (growth rate): 12 μg/L
Test item: Amiodarone Hydrochloride
(Protocol: OECD 201)
(Ref II)
Crustacean (Daphnia magna):
NOEC 21 d (reproduction, mortality): 68.4 μg/L
Test item: Amiodarone Hydrochloride
(Protocol: OECD 211)
(Ref III)
Fish (Pimephales promelas):
NOEC 28 days (survival, growth): 623 μg/L
(Protocol: OECD 210)
(Ref IV)
Other ecotoxicity data:
The PNEC (μg/L) = lowest EC50/10 was calculated using results from the most sensitive toxicity endpoint and an assessment factor of 10 (three long-term results from species representing three trophic levels), to add a safety margin to the toxicity endpoint. The most sensitive species was Pseudokirchneriella subcapitata for which the NOEC 72 h was 12 μg/L.
PNEC = 12 μg/L/10 = 1.2 µg/L
Environmental Risk Classification (PEC/PNEC ratio)
PEC/PNEC= 0.053/1.2 = 0.044
PEC/PNEC ≤ 0.1 which justifies the phrase “Use of amiodarone has been considered to result in insignificant environmental risk”.
Degradation
Biotic degradation
Ready degradability:
Test showed 0% degradation in 28 days (OECD 301B) (Ref V).
Justification of chosen bioaccumulation phrase:
Amiodarone fails to pass the criteria for ready biodegradability which justifies the phrase “Amiodarone is potentially persistent”.
Bioaccumulation
Partitioning coefficient:
Log Pow 7.96 at pH 7
Test item: Amiodarone Hydrochloride
(Protocol: OECD 123)
(Ref VI).
Justification of chosen bioaccumulation phrase:
Since log Pow of 7.96 > 4 at pH 7, the substance has high potential for bioaccumulation.
Excretion (metabolism)
Amiodarone is excreted as <1 % as parent compound in urine and most of it is excreted as metabolites, through feces (Ref VII) (Ref VIII).
Metabolites identified are N-desethylamiodarone (main metabolite), di-N-desethylamiodarone (Ref IX). Metabolites may possess some antiarrhythmic activity (Ref IX).
References
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ECHA, European Chemicals Agency, 2008 Guidance on information requirements and chemical safety assessment.
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Sanofi, internal report: Growth inhibition test with Amiodarone Hydrochloride on Algae (Pseudokirchneriella subcapitata). OECD 201. Report # 12/358-022AL, June 2013.
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Sanofi Internal report: Chlorhydrate Amiodarone: Influence to Daphnia magna in a Semi-Static Reproduction Test. OECD 211. Report 135331221, 2019
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Overturf MD, Overturf CL, Baxter D, Hala DN, Constantine L, Venables B, Huggett DB. 2012. Early life-stage toxicity of eight parmaceuticals to the fathead minnow, Pimephales promelas. 62: 455-464.
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Sanofi, internal report: Determination of the ready biodegradability CO2 evolution test. OECD 301B. Report # 32145 ECS, January 2007.
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Sanofi Internal report: Chlorhydrate Amiodarone: Determination or the Partition Coefficient (n-Octanol/Water) by Slow Stirring Method at pH7. OECD123. Report 135331186, 2019
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Latini R, Tognoni G, Kates RE. 1984. Clinical pharmacokinetics of amiodarone. 9: 136-156.
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Cohen-Lehman J, Dahl P, Danzi S, Klein I. 2010. Effect of amiodarone therapy on thyroid function. Nature Reviews Endocrinology. 6: 34-41.
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HSDB, online review, February 2014: http://toxnet.nlm.nih.gov/cgi-bin/sis/search/f?./temp/~we4XnE:1.