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SCARCE Course
Valencia 7-8 February 2011
Case study: The Guadalquivir River (estuary)
Julián Blasco, Ethel Eljarrat, Damiá Barceló
• General description of the Guadalquivir river
basin
• Studies carried out in the past (focusing to the
estuary)
• Aznalcollar disaster, an event in the estuary
• The Guadalquivir estuary project
• The SCARCE project, new approach to the
study of the river basin
•Length 657 km
•Main water resource
•Subjected to many
inputs
•Navigable up as far as
Seville (90 km
upstream). Pollution
and erosion problems
•The estuary has
additional ecological
value due to the
presence of the
Doñana National Park
(Biosphere reserve)
Contamination studies in the Guadalquivir river estuary
1970-1980
Lack of information. Grey literature
Two research groups from CSIC, IQOG and IRNASE. Studies related to
the levels of organochlorine pesticides, PCBs and mercury in eggs of
birds.
Hernández et al., 1976 study of the river basin (11 sampling stations
between Mogon and Sanlúcar de Barrameda). Organochlorine
contamination and mercury (low levels)
1980-1998
Group of UCO (Rincon, Zurera et al. 1986; Rincón 1986; Jodral et al. 1987; Rincon et al. 1987; Rincón
1987; Zurera 1987; Rincon-Leon et al. 1988).
River basin study but it is focused to metals in the biotic compartment.
Studies about the availability of metals. High levels for Cu and Pb and
intermediate levels for Zn.
The main entry of metals in the Guadalquivir and Doñana
National Park is associated to the Guadiamar river
• Organic contamination was homogenous for Guadiamar river (PCBs
and DDTs levels) were higher than recomended values and it was
related to agriculture and industrial activities. Levels of both
chemcial compounds were detected in aquatic species.
• The presence of pesticides in the Guadalquivir estuary was related
to a seasonal component.
• In 1998, the Regional Governement establish a plan for control
quality of the water in the estuary area (abiotic compartment water
and sediment, organochlorine and organophosphorous compounds;
in sediments PAHs, PCBs 7, 52 153 and180, DDT and DDE)
Aznalcóllar disaster 1998
- One of the main environmental catastrophes in Spain
Reasons
- Magnitud
- Close to the Doñana National Park
The figures of the disaster
•50 m of the dam were broken
• 6 million de cubic meters of muds and
acid waters were dumping to the
Guadiamar river
•3 m of muds were deposited close to the
mine
•25 millones million de cubic meters of
muds and acid waters stayed in the mining
pool
•pH acid waters close to 3
•2.5 Hm3 of acid water went into the
Guadalquivir estuary
Ecosystem impact
•Atmospheric contamination (490 µg/m3)
•Soils (Cu, Zn, As, Cd, Sb, Tl, Pb)
•Groundwater
•Guadiamar (Zn concentrations increased 300
times)
•The Guadalquivir river estuary
Metal levels in“Entremuros”
Zn 230 mg/L
Cd 0,5 mg/L
Tl, Mn, Co y Ni
Without treatment= 300 metric tonns of Zn
2.5 Hm3 acid waters were into the
Guadalquivir river estuary
Zn is the key element
Initial environmental assessment
•Lack of information
•Monitoring of the contamination in environmental
compartments.
Environmental compartments
-Estuary vertically homogenous
-No conservative behaviour
Peninsula Iberica
Rio Agrio
Mine Guadiamar
River
Aznalcóllar
Entremuros Balsa
tratamiento
Sanlúcar de Barrameda
N
5 Km
Parque Nacional De Doñana
Sevilla
1
2 3
4 5 6
1 2 3
4 5 6
Metal Low salinity High salinity
Zn
Cd
Pb
Cu
125 µg/L
0.40 µg/L
15 µg/L
10 µg/L
50 µg/L
0.20 µg/L
7 µg/L
5 µg/L
9.4
2.3
3.2
-0.09
11.9
0.2
3.3
3.6
-53.9
-0.3
-12.2
-15.4
2.5 0.29 1.0 0.4
Metals are accumulated in the lower part of the estuary
BONANZA EL PUNTALETE EL YESO
Zn Cd Pb Cu
Zn
Cd
Pb
Cu
Zn
Pb
Cu
Cd
Zn
Pb
Cu
Cd
Flux of metals in g.s-1
Sediments
Fecha Zn Cd Pb Cu Fe Mn
May 98
St. 2
St. 6
Sept 98
St. 2
St. 6
166
395
109
157
0.58
1.38
0.27
0.46
28.7
33.8
18.4
22.5
18.5
13.1
9.8
11.1
23697
14660
8769
12828
535
412
173
351
mg/kg dry weight
4846
1094
7590
1219
0
1000
2000
3000
4000
5000
6000
7000
8000
pp
m (
dry
weig
ht)
1968 1998
Año
Zn
Cu
1/1/1998 1/7/1998 1/1/1999 1/7/1999 1/1/2000 1/7/2000 1/1/2001 1/7/2001
Zn
(u
g/g
dry
we
igh
t)
0
5000
10000
15000
20000
1/1/98 1/7/98 1/1/99 1/7/99 1/1/00 1/7/00 1/1/01 1/7/01 1/1/02
Cu
(u
g/g
dry
we
igh
t)
-500
0
500
1000
1500
2000
2500
3000
3500
1/1/98 1/7/98 1/1/99 1/7/99 1/1/00 1/7/00 1/1/01 1/7/01 1/1/02
Cd
(ug
/g d
ry w
eig
ht)
0
2
4
6
8
10
12
C. angulata
Zn: 9134 ug/g
dw
Cu: 1460 ug/g
dw.
Cd: 5.45 ug/g
dw
1/1/98 1/7/98 1/1/99 1/7/99 1/1/00 1/7/00 1/1/01 1/7/01 1/1/02
Zn (
ug/g
dry
weig
ht)
0
200
400
600
800
1000
1200
1400
1/1/98 1/7/98 1/1/99 1/7/99 1/1/00 1/7/00 1/1/01 1/7/01 1/1/02
Cu (
ug/g
dry
weig
ht)
0
10
20
30
40
50
60
70
Scrobicularia
plana
Organic compounds
• Presence of mono and dichlorinated and brominated
triphenylamines in the sludge and contaminated soils
• Range 29 ug/g (close to the mine) to 0.14 ug/g (30 km)
• More halogenated compounds were not recorded in water
bodies-high lipophilicity
• Substituted carbazoles were found widespread in surface
water-hydrophilic
• Source of the products –use in ore processing or industrial
waste dumped.
Year 2000
Environmental impact assessment dredging activities Seville harbour
(CIS) • Contamination in sediments of Guadalquivir ( from dock of Seville harbour
to mouth of the Guadalquivir river
• Low levels of metals, high values in the inner of the dock
• Organic contaminants (PCBs and organochlorine pesticides) were found in
the dock and the Guadalquivir river , source agriculture.
• PAHs low levels in all samples
• Evaluation criteria CEDEX recomendations (Action Levels I, II and III)
Estación Boya 9 Boya 13 Boya 14 Boya 18 Boya 28 Boya 34 Boya D.Isaías
Localización 36º 53.357 6º 20.634
36º 54.508 6º 16.444
36º 53.435 6º 14.766
36º 53.435 6º 14.786
37º 01.917 6º 7.817
37º 04.928 6º 7.219
37º 19.064 6º 0.989
Fechas Profundidades 1 2 3 5 7 10 15 20 30
7/03/08 4/06/08 26/11/08 X X X X X X X X X
7/03/08 4/06/08 26/11/08 X X X X X X X X X
7/03/08 4/06/08 26/11/08 X X X X X X X X X
7/03/08 4/06/08 26/11/08 X X X X X X X X X
7/03/08 4/06/08 26/11/08 X X X X X X X X X
7/03/08 4/06/08 26/11/08 X X X X X X X X X
7/03/08 4/06/08 26/11/08 X X X X X X X X X
Organic compounds
Pesticidas organoclorados
HCHs α-HCH, β-HCH, γ-HCH, δ-HCH
DDXs 2,4-DDE, 4,4-DDE, 2,4-DDD, 4,4-DDD,
2,4-DDT, 4,4-DDT
Policlorobifenilos PCBs PCB-28, PCB-52, PCB-101, PCB-118,
PCB-138, PCB-153, PCB-180
Retardantes de llama bromados
PBDEs
di-BDEs (7,10,15), tri-BDEs (17,28,30),
tetra-BDEs (47,49,66,71,77), penta-BDEs
(85,99,100,119,126), hexa-BDEs
(138,139,140,153,154,156,169),
hepta-BDEs (171,180,183,184,191), octa-
BDEs (196,197,201,203,204,205), nona-
BDEs (206,207,208), deca-BDE (209)
non-PBDEs
pentabromoethylbenzene (PBEB),
hexabromobenzene (hexaBBz),
decabromodiphenylethane (deBDethane)
SCARCE project – new approach
• 25 sampling stations in the
river basin
• Priority and emergent
contaminants
• Improve of the knowledge
at river basin level
• Forcing variables related to
global change-effects
• Gaps about occurence and levels of pollutants in the
Guaadlquivir river basin
• Tool for water managers-quality RBMP and PoMs
Acknowledgements
• University of Cádiz (Dpt. Physical-Chemistry and Physical Oceanography
• Ecology of saltmarshes and Intertidal systems and Ecosystem
Oceanography teams from ICMAN (CSIC)
• CSIC and Consejería Medio Ambiente Junta Andalucía
• Autoridad Portuaria Puerto Sevilla
Thank you for you attention