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Universidade de Brasília Departamento de Ecologia. Effects of different land cover on chemical characteristics of streams and flow components in the Cerrado region. José Salomão Silva Universidade de Brasília Daniel Markewitz University of Gerogia
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Universidade de Brasília Departamento de Ecologia Effects of different land cover on chemical characteristics of streams and flow components in the Cerrado region José Salomão Silva Universidade de Brasília Daniel Markewitz University of Gerogia Mercedes Bustamante Universidade de Brasília Richard Zepp US - EPAAlex Krusche Universidade de São Paulo/CENA Roger Burke US - EPA Laerte Guimarães Universidade Federal de Goiás/LAPIG
BrazilianSavanna “Cerrado” • 2ndmostextensiveplantformationoftheLatin America • 2.000.000 km2; • 24% oftheBrazilianterritory; • Where are formed the main basin: • Paraná /Paraguai – 71% • Araguaia /Tocantins – 71% • São Francisco – 94%
Braziliansavanna “Cerrado” • Climate • Precipitation ranges from 750 - 2000mm • Soils • Mostly dystrophic; • About 46% are Oxisols (low pH, high Al, clayey); • 15% are sandy soils.
Open scrubland Open grassland “Campo sujo” “Cerrado ralo” “Cerrado típico” <1% <5% 5-20% Canopy cover index 20-50%
Gallery Forest “Mata de Galeria” • Beside to occupy 5% of the biome, has 45% biodiversity; • Relevant role as buffer zone between terrestrial and aquatic systems; • Although protected by law – very threatened by agricultural and urban development
Land cover in the Brazilian Savanna (2002) Natural area Water mass Agricultural area Cultived grassland Urban area Reforestation Land uses in the Cerrado (hectare) Sano et al. 2008
How these land cover changes affect: STUDY AREA • Stream water quality • Flow components: • Bulk deposition; • Runoff; • Soil solution; • Ground water.
Urban cover: 3 streams Natural cover: 3 streams Rural cover: 3 streams • Watersamplingandanalyses: • Samplingevery 15 daysduringwetseasonand 30 daysduringdryseason, alongtwoyears; • Parameters: • pH, electricalconductivity, alkalinity, turbidityanddissolvedoxygen; • Dissolved Organic Carbon (Carbon analyzer); • Ca+2, Mg+2, K+, Na+, PO4-, Cl- and SO4- (Chromatography); • NO3-, NO2- and NH4+(Chromatography) • Total Dissolved Nitrogen (Persulphate digestion). • Filtered samples
Stream water – pH, alkalinity, conductivity and turbidity pH Alcalinity E.C. Turbidity URBAN > RURAL>NATURAL
Stream water - [O2] and [DOC] DO URBAN > NATURAL> RURAL DOCURBAN>RURAL = NATURAL;
Stream water – [TDN], [NH4+], [NO2-] and [NO3-] TDNURBAN>RURAL =NATURAL NH4+ URBAN= RURAL >NATURAL NO2- and NO3- URBAN > RURAL > NATURAL
Stream water - [Ca+2], [Mg+2], [K+] and [Na+] Ca+2 Mg+2 K+ Na+2 URBAN>RURAL >NATURAL
Stream water – [SO4-] and [Cl-] SO4- Cl- URBAN >RURAL >NATURAL
Conclusion A higher nutrient load in streams near to urban and agricultural areas in relation to natural areas
Flow components • Bulk deposition; • Runoff; • Soil solution; • Ground water. • Natural cover • Rural cover • Watersamplingandanalyses: • Samplingevery 15 daysduringwetseason • and 30 daysduringdryseason, alongtwoyears; • Parameters: • pH, electricalconductivity, alkalinity; • DissolvedOrganicCarbon (Carbonanaliser); • Ca+2, Mg+2, K+, Na+, PO4-, Cl-and SO4-, NO3-, NO2-and NH4+(Chromatography) • Total DissolvedNitrogen (Persulphatedigestion).
Experimental design Forest edge Bulk deposition colector Close to the stream (4 to 20 m) Far from the stream (30 to 140 m). Runoff colector Well Lysimeter Stream
[NH4+ ] Flow components Streams
[NO2- ] Streams Flow components
[NO3- ] Flow components Streams
End-Member Mixing Analysis Flow components: Runoff close to stream Soil solution close to stream Groundwater far from stream Groundwater contributed more than 90%
Conclusions • A higher nutrient load in streams near to urban and agricultural areas in relation to natural areas; • Most of the elements did not show changes in flow components • However, land cover change increased N forms concentrations in flow components, specially in the groundwater