Integrated remote and in situ analysis of a playa lake groundwater system in northern Chile Katherine H. Markovich The University of Texas at Austin Hydrogeology of Arid Environments March 15 th, 2012
o Precipitation: 78.8 mm/yr (88% occurring during summer) o Evapotranspiration: 1630 mm/yr o Mean Temperature: 5.8 C o Elevation: 3700 masl o Salar Size: o Ascotán: 243 km 2 o Carcote: 108 km 2
Why do we care? Image courtesy of Wikimedia Commons
Keller and Soto, 1998
What has been the extent of the climatic and anthropogenic influence on this groundwater system over time? 1) Characterize regional and local behavior using remote sensing. 2) Relate the spatiotemporal variation to climate and/or anthropogenic forcings. 3) Supplement with in situ and hydrochemistry data. 4) Assess implications for future water resource management.
Salar Water Budget ΔV= (P+I GW +I SW ) (ET+O GW +O SW ) ET >> P Simple water budget for salars: ΔV= (I GW ) (ET+O GW ) V=change in volume P=precipitation (rain/snow) I SW =surface water inputs I GW =groundwater inputs ET=evapotranspiration O SW =surface water outputs O SW =groundwater outputs Remote sensing gives us ΔA, which can be related to the groundwater system!
Satellite Data o 14 scenes during 1985-2011 o o o Landsat 4-5 TM and 7 ETM+ from the USGS Archive. Supervised Classification in ERDAS Imagine 2011 Monthly precipitation data during 1984-2011 (Lat: 23-20.5 S, Lon: 68-66 W) Hydrochemistry o ph o Conductivity (µs/cm) o Temperature ( C) o Water depth (m) o Cl/Br (mg/l) -(Risacher et al., 2003) o NASA Tropical Rainfall Measuring Mission (TRMM) archive.
Cumulative Precipitation (mm) Significance of Climate Total Water Extent (km 2 ) Red= La Niña Purple= El Niño 600 500 400 Precip Area 12 10 8 300 6 200 4 100 2 0 1984 1987 1990 1993 1996 1999 2002 2005 2008 2011 0 Houston (2006) study linked precipitation in the region to ENSO cycles Link between increased GW contributions to the salars, precipitation, and La Niña
Caldera Water Extent (km 2 ) Caldera Water Extent (km 2 ) Regional application: Pastos Grandes as a recharge zone for Ascotán? 60 70 50 40 30 60 50 40 30 y = 5.1249x - 10.402 R² = 0.7074 y = 4.0407x - 3.871 R² = 0.2276 20 20 10 10 August, 1985 0 August, 1990 0 0 2 4 6 8 10 12 Salar Water Extent (km 2 ) 0 2 4 6 8 10 12 Salar Water Extent (km 2 )
Salar Water Extent (km 2 ) 12 Current groundwater abstraction is located in the southern portion of Ascotan. Has this affected springs to the north? 10 8 6 y = -0.0004x + 20.94 R² = 0.2741 Total North Ascotan South Ascotan Carcote 4 2 0 1985 1986 1987 1988 1989 1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 Carcote CAR-1 North Ascotán V2 V7 Legend Field Sites Salars V10 South Ascotán 01.252.5 5 7.5 10 Kilometers V11
Integrate remote sensing observations with hydrochemistry analysis. o Water temperature, conductivity, and ph gave no clear indication of regional versus local flow o Cl/Br ratios provide the best indication for spatial relationships o Possible inverse Ghyben-Herzberg flow in the north, causing the recycling of brines
Conclusions 1) Remote sensing allowed for antecedent analysis and large scale observation of regional recharge behavior. 2) Total surface water extent has fluctuated with a clear response to pumping initiation, but also appears to be dominated by precipitation. 3) Integration of hydrochemistry data, namely Cl/Br ratios, provided evidence for disconnect between north and south Ascotán
Future water resource management to take into account: o Ocean circulation cycles o Climate change o New mine projects o Cost-benefit analysis of water importation Next steps: 1) Build systems dynamics models. 2) Compare across multiple salar sites in Chile 3) Incorporate into cyberinfrastructure to support cross-disciplinary and longitudinal studies.
Thank you for listening! Thanks to: Suzanne Pierce, Kelley Crews, Wendy Robertson, Reed Malin, Sandra Guzman, and Jack Sharp for help on the field work and the project François Risacher (U. Strasbourg), Martin Reich (CEGA, U. Chile), Boris (SCM El Abra), and Eugenio Figueroa (U. Chile) for data University of Texas Co-op and Jackson School of Geosciences for funding
Questions?
References Casteñeda, C., Herrero, J., and Casterad, M.A., 2005. Landsat monitoring of playa-lakes in the Spanish Monegros desert. Journal of Arid Environments, v. 63, pp. 497-516. Hartley, A., May, G., Chong, G., Turner, P., Kape, S.J., and Jolley, E.J., 2000. Development of a continental forearc: A Cenozoic example from the Central Andes, northern Chile. Geology, v. 28, pp. 331-334. Houston, J., 2006. Variability of precipitation in the Atacama desert: It s causes and hydrological impact. International Journal of Climatology, v. 26, pp. 2181-2196. Keller, B. and Soto, D., 1998. Hydrogeologic influences on the preservation of Orestias ascotanensis (Teleostei: Cyprinodontidae) in Salar de Ascotán, northern Chile. Revista Chilena de Historia Natural, v. 71, pp. 147-156. Risacher, F., Alonso, H., and Salazar, C., 2003. The origin of brines and salts in Chilean salars: a hydrochemical review. Earth-Science Reviews, v. 63, pp. 249-293. Rodriguez-Rodriguez, M., Benavente, J., Cruz-San Julian, J.J., & Moral Martos, F., 2006: Estimation of ground-water exchange with semi-arid playa lakes (Antequera region, southern Spain --Journal of Arid Environments. 66: 272-289. Xu, H., 2006. Modification of normalised difference water index (NDWI) to enhance open water features in remotely sensed imagery. International Journal of Remote Sensing, v. 27 (14), pp. 3025-3033. Zhou, Y., 2009: A critical review of the groundwater budget myth, safe yield, and sustainability --Journal of Hydrology, v. 370, pp. 207-213.