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Impact of Stockholm Convention
POPs in gull eggs from the Ebro
Delta Natural Park
Silvia Lacorte, Pablo Zapata, Rubén Ballesteros,
Pere Colomer, Mª Generosa Martrat, Esteban
Abad, Albert Bertolero, Javier Santos
Department of Environmental Chemistry, IDAEA-
CSIC, Barcelona
Department of Analytical Chemistry, University of
Barcelona
Associació Ornitològica Picampall de les Terres
de l’Ebre
Flix
0.5 km
21
Erkimia-Ercros (1897-2013)
Chlorine for textile manufacturing
Manufacture of fertilizers (1904)
Manufacture of PCBs (1959-1983)
Manufacture of OC pesticides (1941
1975)
700,000 t of industrial sludge (16 t
PCBs, 7 t HCB, 0.5 t DDTs, 68 t Hg)
Sludge
removed
during
2012-15
25,000 ha
of rice
cultivation
Protected
wetland
(1983)
Ebro delta
Objectives
Sardina sardina
Mytilus
Larus michahellis (high trophic level)
Procambarus
clarkii
• To evaluate the occurrence of
Stockholm Convention POPs in gull
eggs.
• To compare the POPs profile in 2
gull species cohabiting in the same
area.
• To determine the time trends over
the period 2009-2015.
Tools: chemical monitoring to
study the impact of POPs using
gull eggs as bioindicators of
contamination in areas of high
degree of protection
CONTAMINANTED ENVIRONMENT
Landfill
• Long lifespan and site fidelity
• Sensible to chemical pollution 1
• High trophic position 2
• Eggs as non-invasive indicators 3
Larus michahellis and Larus audouinii
Non protected, common,
oportunistic species
Protected, few colonies,
piscivourous
(1) Furness, i col., (1997). ICES J Mar Sci (54), 726-737.
(2) Rüdel, i col., (2010) Environmental Specimen Bank.
(3) Klein, i col., (2012) Environ. Sci. Technol. (46), 5273-5284.
Sampling (2009-2015)
1 6
Biometric parameters recorded
Calculation of eggshell and dissication index CONDITION
Twelve eggs pooled from 3 sites of each colony
Recording of pairs during the period 2005-15 POPULATION
POPs
81 Persistent Organic Pollutants
OCPs
PCBs
SCCPs
PBDEs
PFASs
PCDD/Fa
∑POPs and
profiles
51%
35%
6%
5% 3% 0%
0%
L. michahellis
PCBs
OCPs
PFOS
PBDEs
DL-PCBs
SCCP
PCDD/F
58%25%
7%
6%
4% 0% 0%
L. audouinii
0
500
1000
1500
2000
2500
3000
3500
4000
4500
5000
2009 2010 2011 2012 2013 2014 2015
ng/gww
L. michahellis
L. audouinii
L. michahellis L. audouinii
Trends of PCBs (ng/g ww)
100
0
300
400
500
600
700
200
0
100000
200000
300000
400000
500000
600000
700000
2009
2010
2011
2012
2013
2014
2015
0
200
1400
400
1200
600
1600
800
1000
0
200000
400000
600000
800000
1000000
1200000
1400000
1600000
Larus michahellis
Larus audouinii
OCPs during 2009-15
0
5
10
15
20
25
30
ng/gww
Compounds not detected: aldrin, endrin,
HCHs, heptachlor, methoxychlor, 2,4'-
DDTs, α-chlordane, dicofolL. m
L. a
4,4’-DDE
0
100
200
300
400
500
600
700
800
900
1000
2009
2010
2011
2012
2013
2014
2015
2009
2010
2011
2012
2013
2014
2015
ng/gww
3 4 5 6 7 8 9 10 11 12 13 14 15
Time (min)
0
20
40
60
80
100
0
20
40
60
80
100
RelativeAbundance
10.21
9.93
9.59
9.55
10.45
8.06 9.39 10.589.12
10.938.90
8.407.82 11.117.74 11.517.186.51 12.30 14.0513.24 14.50
9.8910.07
9.82
9.74
10.349.51
9.47
10.56
9.21 10.939.04 11.3111.9312.538.397.776.69 13.4714.06
RelativeAbundance
6.28
6.27
13C6-HCB
13C6-HCB
SCCPs
PFOS
PCDD/Fs and DL-PCBs
PBDEs (predominance BDE 209)
2-6 ng/g ww
0
5
10
15
20
25
30
35
40
PCDD/F DL-PCB PCDD/F+DL-PCB
WHO-TEQpg/gww
L. michahellis
L. audouinii
0
20
40
60
80
100
2009 2010 2011 2012 2013 2014 2015
ng/gww
L. michahellis
L. audouinii
0
10
20
30
40
50
60
70
80
2009 2010 2011 2012 2013 2014 2015
ng/gww
L. michahellis
L. audouinii
BDE
BDE
BDE
BDE
BDE
BDE
BDE
BDE
Standard
Gull egg
Egg and eggshell parameter
EI: measure of shell thinning and productivity
DI: measure of water loss through the shell
Volume: measure of trophic availability
Effect at population level
0
2,000
4,000
6,000
8,000
10,000
12,000
14,000
16,000
18,000
2005 2006 2007 2008 2009 2010 2011 2012 2013 2014
Breedingpairs
Year
Larus michahellis Larus audouinii
Stable
population
(controlled)
Decreasing
population:
- food availability
- weather
- predators
- POPs
Conclusions
• L. michahellis are excellent bioindicators and
reflect the contamination of a given area.
• L. audouinii are similarly affected by POPs
pollution and may reflect the pollution levels of
other bird species sharing habitat.
• ∑POPs may affect the condition of birds and the
population dynamics.
Thank you for your attention

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Ebre2

  • 1. Impact of Stockholm Convention POPs in gull eggs from the Ebro Delta Natural Park Silvia Lacorte, Pablo Zapata, Rubén Ballesteros, Pere Colomer, Mª Generosa Martrat, Esteban Abad, Albert Bertolero, Javier Santos Department of Environmental Chemistry, IDAEA- CSIC, Barcelona Department of Analytical Chemistry, University of Barcelona Associació Ornitològica Picampall de les Terres de l’Ebre
  • 2. Flix 0.5 km 21 Erkimia-Ercros (1897-2013) Chlorine for textile manufacturing Manufacture of fertilizers (1904) Manufacture of PCBs (1959-1983) Manufacture of OC pesticides (1941 1975) 700,000 t of industrial sludge (16 t PCBs, 7 t HCB, 0.5 t DDTs, 68 t Hg) Sludge removed during 2012-15 25,000 ha of rice cultivation Protected wetland (1983) Ebro delta
  • 3. Objectives Sardina sardina Mytilus Larus michahellis (high trophic level) Procambarus clarkii • To evaluate the occurrence of Stockholm Convention POPs in gull eggs. • To compare the POPs profile in 2 gull species cohabiting in the same area. • To determine the time trends over the period 2009-2015. Tools: chemical monitoring to study the impact of POPs using gull eggs as bioindicators of contamination in areas of high degree of protection CONTAMINANTED ENVIRONMENT Landfill
  • 4. • Long lifespan and site fidelity • Sensible to chemical pollution 1 • High trophic position 2 • Eggs as non-invasive indicators 3 Larus michahellis and Larus audouinii Non protected, common, oportunistic species Protected, few colonies, piscivourous (1) Furness, i col., (1997). ICES J Mar Sci (54), 726-737. (2) Rüdel, i col., (2010) Environmental Specimen Bank. (3) Klein, i col., (2012) Environ. Sci. Technol. (46), 5273-5284.
  • 6. 1 6 Biometric parameters recorded Calculation of eggshell and dissication index CONDITION Twelve eggs pooled from 3 sites of each colony Recording of pairs during the period 2005-15 POPULATION POPs
  • 7. 81 Persistent Organic Pollutants OCPs PCBs SCCPs PBDEs PFASs PCDD/Fa
  • 8. ∑POPs and profiles 51% 35% 6% 5% 3% 0% 0% L. michahellis PCBs OCPs PFOS PBDEs DL-PCBs SCCP PCDD/F 58%25% 7% 6% 4% 0% 0% L. audouinii 0 500 1000 1500 2000 2500 3000 3500 4000 4500 5000 2009 2010 2011 2012 2013 2014 2015 ng/gww L. michahellis L. audouinii L. michahellis L. audouinii
  • 9. Trends of PCBs (ng/g ww) 100 0 300 400 500 600 700 200 0 100000 200000 300000 400000 500000 600000 700000 2009 2010 2011 2012 2013 2014 2015 0 200 1400 400 1200 600 1600 800 1000 0 200000 400000 600000 800000 1000000 1200000 1400000 1600000 Larus michahellis Larus audouinii
  • 10. OCPs during 2009-15 0 5 10 15 20 25 30 ng/gww Compounds not detected: aldrin, endrin, HCHs, heptachlor, methoxychlor, 2,4'- DDTs, α-chlordane, dicofolL. m L. a
  • 12. 3 4 5 6 7 8 9 10 11 12 13 14 15 Time (min) 0 20 40 60 80 100 0 20 40 60 80 100 RelativeAbundance 10.21 9.93 9.59 9.55 10.45 8.06 9.39 10.589.12 10.938.90 8.407.82 11.117.74 11.517.186.51 12.30 14.0513.24 14.50 9.8910.07 9.82 9.74 10.349.51 9.47 10.56 9.21 10.939.04 11.3111.9312.538.397.776.69 13.4714.06 RelativeAbundance 6.28 6.27 13C6-HCB 13C6-HCB SCCPs PFOS PCDD/Fs and DL-PCBs PBDEs (predominance BDE 209) 2-6 ng/g ww 0 5 10 15 20 25 30 35 40 PCDD/F DL-PCB PCDD/F+DL-PCB WHO-TEQpg/gww L. michahellis L. audouinii 0 20 40 60 80 100 2009 2010 2011 2012 2013 2014 2015 ng/gww L. michahellis L. audouinii 0 10 20 30 40 50 60 70 80 2009 2010 2011 2012 2013 2014 2015 ng/gww L. michahellis L. audouinii BDE BDE BDE BDE BDE BDE BDE BDE Standard Gull egg
  • 13. Egg and eggshell parameter EI: measure of shell thinning and productivity DI: measure of water loss through the shell Volume: measure of trophic availability
  • 14. Effect at population level 0 2,000 4,000 6,000 8,000 10,000 12,000 14,000 16,000 18,000 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 Breedingpairs Year Larus michahellis Larus audouinii Stable population (controlled) Decreasing population: - food availability - weather - predators - POPs
  • 15. Conclusions • L. michahellis are excellent bioindicators and reflect the contamination of a given area. • L. audouinii are similarly affected by POPs pollution and may reflect the pollution levels of other bird species sharing habitat. • ∑POPs may affect the condition of birds and the population dynamics.
  • 16. Thank you for your attention