atmospheric transport and deposition of pesticides in sweden 9-50.pdf · atmospheric transport and...
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Atmospheric transport and deposition
of pesticides in Sweden
Jenny Kreuger, Martin Larsson & Therese Nanos Swedish University of Agricultural Sciences (SLU), Uppsala, Sweden
Pesticide Behaviour in Soils, Water and Air York, UK 2-4 September 2013
Background
• Long-term monitoring of environmental fate of pesticides in Sweden since 2002 (main focus on surface water and groundwater)
• However, one program also includes atmospheric deposition of pesticides (as well as other parameters such as particles, ozone, nitrogen, mercury etc)
• Overall aim of the pesticide monitoring program is to study the extent of deposition of pesticides via rainwater in rural background areas, incl. long-term trends
Sampling sites
Vavihill (Rainwater+air)
Aspvreten (Rainwater)
• Sampling sites located jointly with other international/national atmospheric monitoring programs (e.g. EMEP)
• Located in rural background areas, surrounded by forests, >1 km from treated fields
• Rain water collected • Event related sampling using a
bulk sampler (a stainless steel funnel, area 0.5 m2, above a fridge)
• Collected in 10 litre bottle • Ca 12-15 samples/season • Blank samples collected
regularly • Start in 2002 at Vavihill and in
2009 at Aspvreten • Main sampling season today
April-October (previously May-June + October)
Methods - rain
Analytical methods
• On-line LC-MS/MS for a broad range of pesticides • Method description Jansson & Kreuger, 2010, J. AOAC
Intern., vol 93, 1732-1747
• GC-MS for the most non-polar compounds
• Currently including ca 130 different pesticides in the monitoring program, incl. some degradation products, corresponds to ca 90 % of the applied amount of pesticides in Sweden, but also some obsolete
• LOD/LOQ levels are at the ng/l-level for most pesticides
Results rain 2002-2012
• 82 pesticides & 7 degradation products were detected in rainwater • 36 herbicides, 26 fungicides & 20 insecticides • 23 of these were banned in Sweden • Fewer pesticides and lower concentrations at
Aspvreten (northeast)
• Most detects at the low ng/l-level, though some were occasionally detected above 0.1 µg/l • prosulfocarb, MCPA, pendimethalin, isoproturon,
bentazone, terbutyhazine-desethyl, metazachlor and protioconazole-destio
• Max concentration - 3.6 µg/l (prosulfocarb)
0% 10%20%30%40%50%60%70%80%90%100%
lindane
endosulfan-alpha
propamocarb
prosulfocarb
chlorpyrifos
endosulfansulfate
MCPA
endosulfan-beta
terbuthylazine-desethyl
fluazinam
metazachlor
terbuthylazine
clomazone
isoproturon
metolachlor
prothioconazole-desthio
diflufenican
fenpropimorph
carbendazim
epoxiconazole
pendimethalin
spiroxamine
azoxystrobin
ethofumesate
cyprodinil
HCH-alpha
vinklozolin
mecoprop
2,4-D
dichlobenil
flu
r
oxypyr
pyraclostrobin
dicamba
Detec onfreq.Vavihill
Detection frequency in rainwater at Vavihill (south) 2002-2012 Of those pesticides detected in ≥ 20% of the samples 45% were not used in Sweden during the investigation period (lindane, endosulfan a+b, terbuthylazin, metolachlor, carbendazim, epoxiconazole, sprioxamin, vinclozolin, 2,4-D, dichlobenil)
0,1 1 10 100
prosulfocarb
MCPA
prothioconazole-desthio
pendimethalin
terbuthylazin-desethyl
isoproturon
terbuthylazin
fenpropimorph
ethofumesate
phenmedipham
metolachlor
propamocarb
metazachlor
epoxiconazole
cyprodinil
azoxystrobin
metamitron
2,4-D
propiconazole
fluroxypyr
diflufenican
spiroxamine
atrazine
aclonifen
Averagedeposi onMay-Jun+Oct2002-2011(µg/m2*year)
= not used in Sweden
Atmospheric deposition via rainwater at Vavihill in southern Sweden 2002-2011 • Herbicides
dominate, followed by fungicides
• Also pesticides not used in Sweden (red bars) contribute to the total load
0.0
0.5
1.0
1.5
2.0
Dep
osi
tio
n (
µg
/m2
) 2,4-D
0.0
0.5
1.0
1.5
2.0
20
02
20
03
20
04
20
05
20
06
20
07
20
08
20
09
20
10
20
11
Dep
osi
tio
n (
µg
/m2
)
atrazine
0.0
0.5
1.0
1.5
2.0
Dep
osi
tio
n (
µg
/m2
)
lindane
Yearly ∑ 3-month deposition (µg/m2) 2002-2011 for pesticides not used in Sweden
0.0
2.0
4.0
6.0
20
02
20
03
20
04
20
05
20
06
20
07
20
08
20
09
20
10
20
11
Dep
osi
tio
n (
µg
/m2
)
terbuthylazine
0
5
10
15
20
25
Dep
osi
tio
n (
µg
/m2
)
pendimetalin
0
50
100
150
200
250
20
02
20
03
20
04
20
05
20
06
20
07
20
08
20
09
20
10
20
11D
epo
siti
on
(µ
g/m
2)
prosulfokarb
0
5
10
15
20
25
Dep
osi
tio
n (
µg
/m2
)
MCPA 60
0
5
10
15
20
25
Dep
osi
tio
n (
µg
/m2
)
isoproturon
Yearly ∑ 3-month deposition (µg/m2) 2002-2011 for pesticides used in Sweden
Back-trajectory analysis
• Is there a correlation between composition of detected pesticides and origin of air-masses?
•In early May 2005 a major rainfall event occurred when air-masses came from the south-west
•Results showed that the deposition included 25 different pesticides, 10 of which were not registered for use in Sweden
•A week later (10 May) another major rain event took place when air-masses came from the north-west
•This time fewer pesticides were deposited, i.e. 15 pesticides, with 5 of these not registered for use in Sweden
Conclusions
• Currently used pesticides are regularly detected at ng/l-levels in rainwater, with occasional µg/l-level findings
• A larger number of pesticide detected during spring/early summer, however higher concentrations were detected during fall (mainly prosulfocarb)
• Deposited amount corresponds to ca 0.1-0.0001% of the applied dose in the field
• A significant contribution to atmospheric deposition in southern Sweden from pesticides not used within Sweden, i.e. a transboundary atmospheric transport of pesticides
• Lindane and atrazine, now banned within the EU, were detected at decreasing concentrations
Thank you! Questions?
Acknowledgement:
• The national pesticide monitoring programme is funded by the Swedish Environmental Protection Agency
• Information about the monitoring program for pesticides at www.slu.se/ckb (Centre for Chemical Pesticides)