H33B-05 Esteban G Water subsidies from mountains to deserts: groundwater-fed oases in a sandy landscape Marcelo D Pablo E http:// gea.unsl.edu.ar CONICET – GEA & Universidad Nacional.
Download ReportTranscript H33B-05 Esteban G Water subsidies from mountains to deserts: groundwater-fed oases in a sandy landscape Marcelo D Pablo E http:// gea.unsl.edu.ar CONICET – GEA & Universidad Nacional.
H33B-05 Esteban G Water subsidies from mountains to deserts: groundwater-fed oases in a sandy landscape Marcelo D Pablo E http:// gea.unsl.edu.ar CONICET – GEA & Universidad Nacional de San Luis, ARGENTINA CONICET – Instituto de Nivologia y Glaciologia, ARGENTINA Dept Biology & Nicholas School of the Env. – Duke University, USA * Jackson he Central Monte desert (~120,000 km2) hosts vast sandy aeolian plains dominated by short shrublands. In some areas low landscape positions are occupied by unusually high and dense woodlands of Prosopis flexuosa. Next to the Andean Cordillera, the Central Monte receives large inflows of snowmelt from the San Juan, Mendoza, and Tunuyan rivers, which sustain ~7000 km2 of vineyards and olive orchards. Transverse dunes and discontinuous valleys create elevation gradients of 8 to 20 m. Precipitation is 156 mm/yr (>80% summer-fall). Mean annual temperature is 18.5ºC. Local settlers live in “puestos” around hand-dug wells that supply both people and livestock. The area is grazed by goats and cattle. Large Prosopis trees provide goats with forage, and people with timber and food (flour from seeds, syrup from seedpod carpels) the system What are the contributions of LOCAL rainfall vs. REMOTE mountain snowmelt to groundwater RECHARGE in the sand dune systems of the MONTE DESERT? A• • shrublands in dune crests rainfall: 150 mm/yr Altos Limpios B Water-Soil-Plant sampling * Groundwater sampled at existing handdug wells and ad-hoc bore holes * Ten rainfall events collected in study area + GNIP database for Mendoza * Soil/sediment profiles (5-10 m deep ) done with hand augers * Plant xylem sap-water collected in two dates (woody stem sections saved in vials). • interdune woodlands post with well 1980 toyota truck APPROACHES large & productive Prosopis flexuosa trees -15 -10 -5 0 10 -25 -20 -15 -10 -5 1 0 depth (m) -75 groundwater (bare interdunes) -100 -125 groundwater (vegetated interdunes) vegetated intedune vegetated crest bare interdune δ 18O‰ -15 δ 2H‰ 500 24 0 10 20 30 40 50 site C site B 5 6 site C site A 1 2 3 4 5 6 12 24 0 0.2 0.4 0.6 2 site A, veg. upland site A, bare interdune 6 site A, veg. upland site A, bare interdune 7 vertical profiles of moisture (gravimetric) and chloride (pore water concentration). Note interrupted Y moisture axis expanding range towards saturation in the capillary fringe. Water table position shown with horizontal dashed lines. non-capillary water - RAINFALL wet season dry season -10 -15 Larrea divaricata Prosopis alpataco Capparis atamisquea -5 0 -5 947 site A, vegetated interdune 948 949 705 950 706 951 707 site C, vegetated interdune Intradiurnal level fluctuations (night raise, day drop) are associated with groundwater consumption by plants. Based on their depth and duration throughout the year water uptake can be estimated. In our case suggesting a value of 296 mm/yr. Fluctuations disappear in bare dunes or after rainfall events that provide a more accessible water source to plants. non-capillary water - RAINFALL WEST -15 -20 capillary water - GROUNDWATER EAST crops lowland Xylem sap water isotopic composition at site C. Horizontal colored bands represent 5% to 95% percentiles of soil moisture δ18O‰ values within the unsaturated zone (non-capillary water) and the capillary fringe (capillary water). Markers indicate sap water values of individual plants (2-3 stems per individual) grouped by species and by sampling date. The first sampling date (wet) corresponds to the end of the growing season of 2005-2005 and the second (dry) to the end of the dry season of 2006, before the onset of the next rainfall period. upland bare dune Free aquifer irrigated oasis sand dunes Desaguadero river Infiltration of Andean water brought by the Mendoza River was the dominant mechanism of groundwater recharge. Local recharge was negligible, except in rare bare dune areas. Woodlands in interdune positions displayed significant consumption of groundwater located 6 to 10 m underground. Plants in the rest of the landscape (90% of the area) relied on rainfall. Regional scaling suggests that groundwater evapotranspiration reaches 18 to 42 mm/yr across the whole landscape, accounting for 7 to 17% of the Mendoza river flow regionally. precipitation evapotranspiration surface flow 0.8 0.6 0.4 0.2 0.0 -0.2 -0.4 -0.6 -0.8 water fluxes and trade-offs in the mountain –desert continuum Atlantic moisture (rain in summer) wet season 708 time of the day (hh:mm) Monte Desert dry season -10 583 585 Andes Pacific moisture (snow in winter) 51 mm at site A 584 Hourly dynamics of water tables captured by pressure transducers. The simultaneous water table depth variations at the vegetated interdunes of site C and the neighbouring vegetated and bare interdune of site A are shown. The Y axis indicates relative depth changes and is not intended for absolute level comparisons across sites. Points indicate actual half-hourly measurements and lines three-hour centered moving averages. The occurrence of a large rainfall event is depicted by a horizontal bar at the top. 3 site C, 4 veg. upland site A, bare interdune 952 site C, veg. upland 1 582 CREST plants grasses Larrea divaricata Bulnesia retama Prosopis flexuosa 12 0 Soil water samples grouped according to landscape situations and differentiated by their vertical position in the profile (unsaturated zone vs. capillary fringe) and their gravimetric moisture content (dry < 1.3%, wet > 1.3%) in the case of the unsaturated zone. -150 Isotopic survey. Precipitation events, sampled at the town of Mendoza and at the study are in Telteca. Mendoza and San Juan rivers sampled at their lowest sections before entering the study area. Two temporary ponds were sampled at site. Detailed isotopic composition of river and groundwater samples indicating values for each sampling date. δ18O‰ 6 4 5 INTERDUNE plants 5 site B 0 unsaturated, dry unsaturated, wet capillary fringe -125 hand dug wells 4 vegetated crests & bare interdune Tricomaria usillo Site C bare interdune grasses Site B soil water vegetated interdunes 3 10 depth (m) ground waters Site A 2 9 -100 Site A 1 site A rivers -20 Irrigated oases 8 -175 Mendoza San Juan 100 km 7 -150 -175 GW discharge area River sampling points 3 -50 > 60 mm Water table monitoring * Levels monitored in ad-hoc boreholes with automated pressure transducers with built-in dataloggers (HOBO-Onset water level logger) * Water use estimates based on level fluctuations assumed specific yield of 0.3 mm/mm pore water chloride (g/L) 2 -25 30-60 mm -150 -25 moisture (% mass) 0 ephemeral ponds precipitation events < 30 mm -125 0 10 0 -100 Xylem sap isotopes revealed the combined use of rainfall and groundwater in most species in INTERDUNE woodlands. Rainfall was the only source for plants in the DUNE CREST 5 25 -75 Water level fluctuations suggest frequent groundwater consumption in vegetated interdunes (~300 mm/yr) 0 25 2H‰ -50 In vegetated dunes LOCAL rainfall supplied only upper soil layers with virtually no deep drainage. Bare dunes, instead, experienced deep drainage & local recharge. epilogue 5 50 Sample prep. & analysis * Soil & plant water extracted with azeotropic distillation * Isotopic concentrations analyzed with Finnigan MAT Delta Plus XL (precision +/- 1.5 and 0.1 ‰ at one SD for 2H and 18O, respectively) * Chloride analyzed with ion selective electrode vegetated interdunes δ 18O‰ 50 -25 Shallow phreatic groundwater was recharged by REMOTE snowmelt waters brought from the ANDES by the Mendoza river. 0 woodlands = 10% landscape C • Altitude a.s.l. (m) > 4500 Permanent rivers Temporary rivers ARGENTINA 50 0 δ -20 study sites •dunes with hand-dug wells woodlands 0 1 2 km CHILE shallow groundwater (6-12 m in interdunes) δ 18O‰ -25 Dominant Prosopis used 50% and 90% groundwater in the wet and dry season, respectively groundwater and Prosopis trees are a critical water and food source for people and livestock large trees in interdune groundwater depth from surface (cm) Region: stable isotopic survey of water from rivers, rainfall, groundwater and soils (3 years, Mendoza river watershed) Landscape: deep soil profiles (moisture/isotopes/chloride) across topographic gradients (3 crest-interdune-crest transects) Stand: water table level monitoring (2-3 years, 3 sites) and water stable isotopes in plants (2 dates, 1 site) VERY large isotopic contrasts facilitated our exploration of sources Study region City of Mendoza MATERIALS & METHODS bare dune area x Headquarters of Telteca Reserve City of San Juan What is the contribution of GROUNDWATER to sustain VEGETATION in sand dune landscapes (when, where, how much)? findings [email protected] STUDY REGION In arid regions throughout the world, shallow phreatic aquifers feed natural oases of much higher productivity than would be expected solely from local rainfall. While local groundwater recharge is feasible in arid regions under very sandy soils, transfer from adjacent areas with more positive water balance is another possible recharge source Bulnesia retama Prosopis flexuosa quick tour * Villagra Robert B QUESTIONS quick tour * Nosetto intradiurnal depth deviation (cm) intro * Jobbágy In central Argentina, like in many mountain – desert contact zones of the World, water is increasingly diverted for irrigated agriculture. While the trade-offs between production and SURFACE WATER-fed natural ecosystems is usually obvious, it is less so in the case of GROUNDWATERfed ones, like those studied here. We find signs of a long-term decline of water table levels (dead shell beds, narrower tree rings, historic documents) at our sites, yet their connection with irrigation upstream is still uncertain. EGJ-MDN-PEV-RBJ ground flow The West-East transect encompasses the Andean Cordillera and the Monte Desert with the irrigated oasis of Mendoza and the sand dune landscapes occupied by natural vegetation. The main findings of this work, based on isotopic surveys, deep soil profiles, and water table records, suggest the prevalence of the hydrological fluxes indicated with the arrows. The free aquifer found under the sand dune area is recharged by the Mendoza river (Pacific isotopic signature), likely after it leaves the irrigated area. Upland vegetation is sustained by local precipitation inputs (Atlantic isotopic signature), while lowland vegetation consumes both local precipitation and remotely recharged groundwater. The free aquifer receives no local recharge in the sand dunes with the exception of bare dune zones, as suggested by deep soil profiles and isotopic data. The sand dune region exports a fraction of its groundwater inputs to the Desaguadero river, likely facilitating salt evacuation from the groundwater fed oases. The onset of irrigation could have potentially compromised lowland oases by cutting the contributions of the Mendoza river to the free aquifer, causing declines in water table level and supply to plants. However, the timing of these potential effects is unknown a needs to be resolved to project the impacts of irrigation on natural oases. Evaporative (curved lines) and liquid (straight lines) water fluxes are differentiated.