Miljöpåverkan
Fesoterodin
Miljörisk:
Användning av fesoterodin har bedömts medföra försumbar risk för miljöpåverkan.
Nedbrytning:
Fesoterodin bryts ned i miljön.
Bioackumulering:
Fesoterodin har låg potential att bioackumuleras.
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Detaljerad miljöinformation
Physical properties
Molecular weight1: 411.59 (free base)
Solubility in water1: Fesoterodine fumurate = 542 x 106 µg/L
Fesoterodine free base = 0.5 x 106 µg/L
pKa1: 10.3
Vapor pressure (calculated)2: 9.62 x 10-12 mmHg
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 = 0.000579 μg/L
Where:
A = |
4.228 kg (total sold amount API in Sweden year 2020, data from IQVIA)3. |
R = |
0% removal rate (worst case scenario) |
P = |
number of inhabitants in Sweden = 10 * 106 |
V (L/day) = |
wastewater volume per capita and day = 200 (ECHA default)4 |
D = |
factor for waste water dilution by surface water flow = 10 (ECHA default)4 |
Predicted No Effect Concentration (PNEC)
Ecotoxicological studies
Green alga (Scenedesmus subspicatus) (guideline OECD 201)5
EC50 72 h (growth rate, chronic toxicity) = 34 000 μg/L
EC10 72 h (growth rate, chronic toxicity) = 12 000 μg/L
Daphnids (Daphnia magna) (guideline OECD 211)6
LOEC 21 days (reproduction, chronic toxicity) = 10 000 μg/L
NOEC 21 days (reproduction, chronic toxicity) = 3 200 μg/L
Zebra fish (Brachydanio rerio) (guideline OECD 210)7
LOEC 35 days (reproduction, chronic toxicity) = 11 500 μg/L
NOEC 35 days (reproduction, chronic toxicity) = 3 900 μg/L
Based on the lowest NOEC for the species Daphnia magna and using the assessment factor8 of 10, the PNEC is calculated to 3 200/10 = 320 µg/L.
Environmental risk classification (PEC/PNEC ratio)
PEC/PNEC = 0.000579 / 320 = 1.81 x 10-6, i.e. PEC/PNEC ≤ 0.1 which justifies the phrase ”Use of fesoterodine has been considered to result in insignificant environmental risk.”
Adsorption (guideline OECD 106)9
Soil |
Foc (%) |
Kd (L/Kg) |
KOC (L//kg) |
Speyer 2.2 |
2.29 |
2.9 |
127 |
Mechtildshausen |
1.36 |
5.8 |
424 |
Mussig |
4.13 |
9.0 |
218 |
Bretagne 1 |
2.00 |
3.8 |
189 |
Mean |
5.4 |
239 |
Degradation
Biotic degradation
Water-sediment transformation simulation (guideline OECD 308)10
Length of study: 102 days
Sediment extraction solvent: Extracted with acetonitrile/water (4:1; v/v; up to three times). From sampling day 7 onwards, Soxhlet extraction using the same solvent mixture was performed for at least 4 hours.
Supplemental extraction solvents: Day 102 supplemetal extraction using acetonitrile / 0.1 M hydrochloric acid (1:1; v,v) under reflux conditions for about 4 hours but due to a low amount of radioactivity, no analysis was performed.
The results from the study are shown in the table below.
Data on day 102 at 20 °C |
Rhine river |
Möhlin pond |
Total system |
||
Half-life (days) |
4.91 |
8.46 |
Total 14CO2 (% of AR) |
67.4 |
67.2 |
% Parent (% of AR) |
1.6 |
0.7 |
Aerobic Water Layer |
||
Half-life (days) |
1.5 |
2.4 |
Parent (% of AR) |
0.0 |
0.0 |
Sediment Layer |
||
Half-life (days) |
17.7 |
11.0 |
Bound/NER (% of AR) |
17.1 |
18.2 |
Extractables (% of AR) |
4.2 |
7.6 |
Parent (% of AR) |
1.6 |
0.7 |
ND = not detected, NER = non-extractable residues, AR = applied radioactivity
Justification of chosen degradation phrase
As the total system DT50 value (water-sediment transformation simulation, OECD 308) was calculated to <32 days, it corresponds to the degradation phrase ”fesoterodine is degraded in the environment.”
Bioaccumulation
Partitioning coefficient (guideline OECD 107)11
pH |
Log Kow |
5 |
-3.3 |
7 |
0.0 |
9 |
1.8 |
Justification of chosen bioaccumulation phrase
Since log Dow < 4 at pH 7, fesoterodine has low potential for bioaccumulation.
References
-
Study report A66576: Determination of the partition coefficient (n-octanol/water) of SPM 7605. March 2007.
-
EPI Suite. EPA Office of Pollution Prevention Toxics and Syracuse Research Corporation (SRC).
-
IQVIA KG Consumption 2020 report.
-
ECHA, European Chemicals Agency. 2016 Guidance on information requirements and chemical safety assessment chapter R16.
-
Study report A66644: SPM 7605: Toxicity to Scenedesmus subspicatus in a 72-hour algal growth inhibition test. December 2006.
-
Study report A66666: SPM 7605: Effect on survival and reproduction of Daphnia magna in a semi-static test over three weeks. March 2007.
-
Study report A66688: SPM 7605: Toxic effects to zebra fish (Brachydanio rerio) in an early‑life stage toxicity test. May 2007.
-
ECHA, European Chemicals Agency. 2008 Guidance on information requirements and chemical safety assessment chapter R10.
-
Study report A66622: [14C]-SPM 7605: Adsorption/desorption on soils. June 2007.
-
Study report A66633: [14C]-SPM 7605: Route and rate of degradation in aerobic aquatic sediment systems. June 2007.
-
Study report A66576: Determination of the partition coefficient (n-octanol/water) of SPM 7605. March 2007.