Miljöpåverkan
Vareniklin
Miljörisk:
Användning av vareniklin har bedömts medföra försumbar risk för miljöpåverkan.
Nedbrytning:
Vareniklin bryts ned långsamt i miljön.
Bioackumulering:
Vareniklin har låg potential att bioackumuleras.
Läs mer
Detaljerad miljöinformation
Physical properties4
Solubility at pH 4-10: |
>100 x 106 µg/L pKa: 9.2 |
Vapor pressure at 25 °C: |
Estimated at <1x10-7 mmHg |
Molecular weight: |
361.35 (varenicline tartrate) 211.26 (varenicline) |
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 = 2.08 x 10-4 μg/L
Where:
A = |
1.67 kg (total sold amount API in Sweden year 2020, data from IQVIA)3. |
R = |
9% removal rate as calculated with SimpleTreat 4.0 using an activated sludge sorption coefficient (Kd) of 26 and elimination rate constant (kbiodeg) of 0.011 per hour (Reference OECD 106 & OECD 314B) |
P = |
number of inhabitants in Sweden = 10 * 106 |
V (L/day) = |
wastewater volume per capita and day = 200 (ECHA default)1 |
D = |
factor for waste water dilution by surface water flow = 10 (ECHA default)1 |
Predicted No Effect Concentration (PNEC)
Ecotoxicological studies
Green alga (Pseudokirchneriella subcapitata) (guideline OECD 201)5
EC50 72 h (growth rate, chronic toxicity) = > 6 200 μg/L
NOEC 72 h (growth rate, chronic toxicity) = 1 500 μg/L
Daphnids (Daphnia magna) (guideline OECD 202)6
EC50 48 h (mobility & mortality, acute toxicity) = 240 μg/L
NOEC 48 h (mobility & mortality, acute toxicity) = 130 μg/L
Daphnids (Daphnia magna) (guideline OECD 211)7
LOEC 21 days (reproduction & growth, chronic toxicity) = 20 μg/L
NOEC 21 days (reproduction & growth, chronic toxicity) = 10 μg/L
Daphnids (Ceriodaphnia dubia) (guideline EPA 1002.0)8
LOEC 7 days (reproduction, chronic toxicity) = 5.0 µg/L
NOEC 7 days (reproduction, chronic toxicity) = 2.7 µg/L
Rainbow trout (Oncorphynchus mykiss) (guideline OECD 203)9
LC50 96 h (mortality, acute toxicity) = 48 000 μg/L
NOEC 96 h (mortality, acute toxicity) = 20 000 μg/L
Based on the lowest NOEC for the species Ceriodaphnia dubia and using the assessment factor2 of 10, the PNEC is calculated to 3/10 = 0.27 µg/L.
Environmental risk classification (PEC/PNEC ratio)
PEC/PNEC = 2.08 x 10-4 / 0.27 = 7.7 x 10-4, i.e. PEC/PNEC ≤ 0.1 which justifies the phrase ”Use of varenicline has been considered to result in insignificant environmental risk.”
Adsorption (guideline OECD 106)10
Solid |
Kd (L/Kg) |
Koc (L/Kg) |
Activated sludge |
26 |
74 |
HOM soil (clay loam, MCL-PF) |
254 |
7050 |
HOM soil (sandy clay loam, MSL-PF) |
193 |
9220 |
LOM soil (loamy sand, Roger Myron) |
117 |
8960 |
LOM soil (clay, Montana Clay) |
117 |
16700 |
HOM = high organic matter, LOM = low organic matter
Degradation
Biotic degradation
Water-sediment transformation simulation (guideline OECD 308)11
Length of study: 100 days
High organic sediment system: Turkey creek
Low organic sediment system: Choptank river
Sediment extraction solvent: Two extractions with acetonitrile (ACN) acidified with 0.1N hydrochloric acid
Supplemental extraction solvents: At day 100, an two additional extractions with unacidified ACN
The results from the study are shown in the table below.
Data on day 100 at 20°C |
Turkey Creek |
Choptank River |
Total system |
||
Half-life (days) |
31.7 |
43.8 |
Total 14CO2 (% of AR) |
0.1 |
0.5 |
% Parent (% of AR) |
30.8 |
30.0 |
Aerobic Water Layer |
||
Half-life (days) |
22.1 |
21.7 |
Parent (% of AR) |
11.4 |
6.7 |
Sediment Layer |
||
Bound/NER (% of AR) |
51.3 |
51.0 |
Extractables (% of AR) |
20.0 |
25.5 |
Parent (% of AR) |
19.4 |
23.3 |
ND = not detected, NER = non-extractable residues, AR = applied radioactivity
WWTP degradation (guideline OECD 314B)12
Length of study: 28 days
Parent compound remaining at the end of the study: 25.71 %
Total mineralisation: 0.68 %
Non-extractable residue: 8.95 %
Elimination rate k-value: 0.011 per hour
Loss of parent DT50: 2.6 days
Abiotic degradation
Photolysis (OECD Guideline for Testing of Chemicals, Proposal for a New
Guideline in August 2000)13
The environmental photolytic half-life (t½) of varenicline at 40 degrees north latitude was determined to be rapid at 22.6 and 103 minutes during the summer and winter seasons, respectively.
Justification of chosen degradation phrase
As the total system DT50 value (water-sediment transformation simulation, OECD 308) was calculated to <120 days, it corresponds to the degradation phrase ”varenicline is slowly degraded in the environment.”
Bioaccumulation
Partitioning coefficient (guideline OECD 107)14
pH |
Log Dow |
5 |
-1.23 |
7 |
-0.817 |
9 |
0.758 |
Justification of chosen bioaccumulation phrase
Since log Dow < 4 at pH 7, varenicline has low potential for bioaccumulation.
References
-
ECHA, European Chemicals Agency. 2016 Guidance on information requirements and chemical safety assessment chapter R16.
-
ECHA, European Chemicals Agency. 2008 Guidance on information requirements and chemical safety assessment chapter R10.
-
IQVIA KG Consumption 2020 report.
-
Champix environmental risk assessment. September 2005.
-
Study report 260A-155: Varenicline: A 72-hour toxicity test with the freshwater alga (Selenastrum capricornutum). March 2005.
-
Study report 260A-153: Varenicline: A 48-hour static acute toxicity test with the cladoceran (Daphnia magna). January 2006.
-
Study report 2438.6536: Varenicline (CP-526,555-18) – Full life-cycle toxicity test with water fleas, Daphnia magna, under static-renewal conditions. September 2010.
-
Study report 2438.6468: Varenicline (CP-526,555-18) – The life-cycle toxicity test with daphnids, Ceriodaphnia dubia, under static-renewal conditions. January 2006.
-
Study report 260A-154: Varenicline: A 96-hour static acute toxicity test with the rainbow trout (Oncorhynchus mykiss). January 2006.
-
Study report 260E-162: [14C] varenicline: Adsorption/desorption characteristics in representative soils. December 2005.
-
Study report 260E-158: [14C] varenicline: Aerobic and anaerobic transformation in aquatic sediment systems. January 2006.
-
Study report 260E-159: Varenicline: Dieaway in activated sludge. December 2005.
-
Study report 260C-112: Phototransformation potential of varenicline. September 2005.
-
Study report 260C-114: Varenicline: Determination of the n-octanol/water partition coefficient by the shake flask method. December 2005.