Presentación de PowerPoint poste… · Land Use Land Cover as a consequence and a driver for soil...
Transcript of Presentación de PowerPoint poste… · Land Use Land Cover as a consequence and a driver for soil...
Land Use Land Cover as a consequence and a driver for soil quality changes Cordovil, C M d S1, Marinheiro J1, Vale M J2, Reis R2, Dalgaard T3, Hutchings NJ3 1 Universidade de Lisboa, Instituto Superior de Agronomia, LEAF, Tapada da Ajuda, 1349-017 Lisboa, Portugal 2Direção Geral do Território, Rua Artilharia Um, 107, 1099-052 Lisbon, Portugal 3 Department of Bioscience, Aarhus University, Vejlsovej 25, 8600, Silkeborg, Denmark
Intr
od
uct
ion
• Land use and land cover changes are directly related to soil use and can therefore be associated to soil organic matter depletion and water contamination with nitrates.
• These and other factors that may alter water and soil quality. • Changes in land use are a result of external drivers mainly related to urban growth, agricultural and livestock
production policies, aligned with economic growth and food requirement increase.
Agriculture Livestock Urban
Met
ho
ds • Data about historical land use land cover uses in Portugal was officially produced covering the last decades. This data
are being analysed and combined with other soil use data, agricultural practices integrated in official databases, in order to find potential drivers for soil use change impact on water quality related to reactive nitrogen.
• These integrated datasets are being analysed to select drivers that better explain soil use evolution and related impacts
on soil and water quality in Portugal mainland (located in Tagus river basin – Zêzere watershed)
Re
sult
s C
on
clu
sio
ns
Nitrogen pollution from urban, agriculture and livestock discharges is a main environmental pressure on watersheds within the Tagus river basin, namely in the Zêzere case study.
Pressure evaluation is particularly relevant in watersheds with drinking water catchment, which is the case of Zêzere, responsible for 1/5 of the Portuguese drinking water supply.
Evaluating this pressure is relevant and difficult and must make use of the different available datasets, and monitoring methodologies.
Acknowledgements. Authors thank the NitroPortugal, H2020-TWINN-2015, a Coordination & support action n. 692331 project for funding.
Artificial areas per capita (1990) per municipality around the selected river basin (Zêzere watershed)
Land use change (urban/artificial) between 1990 and 2012 for the Zêzere watershed (part of Tagus river basin).
Artificial surfaces evaluation (COS-soil use; CLC-Corine Land Cover)
Monitoring pressures of different uses, which impact on drainage into the Tagus/Zêzere river basin, with a watershed approach. .
y = 59,907ln(x) - 180,3 R² = 0,2139
y = 160,02ln(x) - 610,79 R² = 0,4675
0
100
200
300
400
500
600
700
800
0 100 200 300 400 500 600 700 800
CO
S (h
a)
CLC (ha)
CLC90/COS90 CLC2012/COS2010
0,000
0,005
0,010
0,015
0,020
0,025
0,030
0,035
0,040
0,045
0,050
AP
ELA
ÇÃ
O
BO
BA
DEL
A
BU
CEL
AS
CA
MA
RA
TE
FAN
HÕ
ES
FRIE
LAS
LOU
RES
LOU
SA
MO
SCA
VID
E
PO
RTE
LA
PR
IOR
VEL
HO
SAC
AV
ÉM
SAN
TA IR
IA D
E A
ZOIA
SAN
TO A
NTÃ
O D
O T
OJA
L
SAN
TO A
NTÓ
NIO
DO
S C
AV
ALE
IRO
S
SÃO
JO
ÃO
DA
TA
LHA
SÃO
JU
LIÃ
O D
O T
OJA
L
UN
HO
S
ha
pe
r ca
pit
a
1990
Objective Evaluate land use land cover changes impact on water and soil quality .
Impact of urban/artificial areas on water quality monitoring parameters