Table 3 Data for groundwater recharge rate study
Author | Soil texture | Aridity index | Location of study area | Period of study (years) | Latitude | Longitude | Method used | Precipitation (mm/year) | Potential evaporation (mm/year)a | Type of natural vegetation | Type of vegetation after change |
|---|---|---|---|---|---|---|---|---|---|---|---|
Huang et al. (2013) | Â | 0.497 | Hequan, Guyan, China | 130 | 35.9 | 106.25 | Muttiple tracers (chloride mass balance, stable isotopes, tritium and water chemistry) | 450 | 906 | Grassland | Winter wheat |
Huang and Pang (2010) | Â | 0.481 | Guyuan, China | 100 | 30.1 | 104 | Chloride-mass balance | 500 | 1040 | Grassland | Winter wheat |
Huang and Pang (2010) | Â | 0.501 | Xifeng Loess Plain, China | 7 | 30.1 | 104.5 | Chloride-mass balance | 523 | 1044 | Winter wheat | Apple |
Allison et al. (1990) | Sand | 0.213 | Western Murray Basin, Australia |  | −34.3 | 139.6 | Groundwater model | 300 | 1245 | Mallee | Cropland |
Allison et al. (1990) | Sandy loam | 0.262 | Western Murray Basin, Australia |  | −35.1 | 140.3 | Groundwater model | 370 | 1346 | Mallee | Cropland |
Allison and Hughes (1972) |  | 0.631 | Western Murray Basin, Australia |  | −37.8 | 140.8 | Tritium method | 686 | 1132 | Mallee | Grassland |
Allison and Hughes (1983) |  | 0.236 | South Australia |  | −35.1 | 142.1 | Chloride method | 335 | 1379 | Mallee | Wheat cropland |
Scanlon et al. (2005) |  | 0.331 | High plains (HP1) in South High Plains, the USA |  | 32.9 | −102.1 | Matric potential, environmental tracers and water table fluctuations and trends in groundwater solutes | 500 | 1670 | Creosote bush and saltbush | Alfalfa |
Scanlon et al. (2005) |  | 0.291 | High plains (HP 2) in South High Plains, the USA |  | 32.9 | −102.1 | Matric potential, environmental tracers and water table fluctuations and trends in groundwater solutes | 440 | 1670 | Creosote bush and saltbush | Alfalfa |
Scanlon et al. (2005) |  | 0.302 | High plains (HP 3) in South High Plains, the USA |  | 32.9 | −102.1 | Matric potential, environmental tracers and water table fluctuations and trends in groundwater solutes | 457 | 1670 | Creosote bush and saltbush | Alfalfa |
Santoni et al. 2010 | Sandy loam | 0.350 | Central Argentina | > 30 years | −33.6 | −65.8 | Residual moisture flux (RMF) and chloride front displacement (CFD) | 518 | 1371 | Dry forest | Crops (dryland agriculture) |
Santoni et al. (2010) | Sandy loam | 0.368 | Central Argentina | > 30 years | −33.5 | −65.8 | Residual moisture flux (RMF) and chloride front displacement (CFD) | 542 | 1371 | Dry forest | Crops (dryland agriculture) |
Santoni et al. (2010) | Sandy loam | 0.370 | Central Argentina | > 30 years | −33.4 | −65.9 | Residual moisture flux (RMF) and chloride front displacement (CFD) | 538 | 1383 | Dry forest | Crops (dryland agriculture) |
Santoni et al. (2010) | Sandy loam | 0.295 | Central Argentina | > 30 years | −33.4 | −66.5 | Residual moisture flux (RMF) and chloride front displacement (CFD) | 447 | 1383 | Dry forest | Crops (dryland agriculture) |
Leduc et al. (2001) | Â | 0.266 | Southwest Niger | Â | 13.6 | 2.6 | Â | 557 | Â | Natural bush | Crops |
Lebel et al. (2009) |  |  | Niamey (Southwest Niger) | 1990–2009 | 2.5 | 14.7 |  | 520 |  | Grassland | Millet |
Allison et al. (1983) | Sand | 0.263 |  |  | −35.11 | 140 | Cores of material in the saturated zone were taken from depths of from 9 to 15 m beneath native and cropped land. Analyses made of water content and chloride, stable isotopes, and tritium. | 335 | 1379 | Eucalyptus scrub (mallee) | Cropped wheat-fallow |
Allison et al. (1985) | Â | 0.217 | Murray Basin, South Australia | Â | Â | Â | Chloride mass balance and tritium dating | 300 | 1374 | Native mallee vegetation | Poorly developed pasture cleared in the 1930s |
| Â | 0.288 | Karstic region of southern Australia | Â | Â | Â | Â | 632 | Â | Plantation forest of Monterey pine | Grassland | |
Gee et al. (1992) | Sand | 0.153 | 200 East | 1971–1985 change 1988–1989 | 46.6 | −119.4 | Lysimeter | 168 | 1083 | Tumbleweed | Bare |
Cook et al. (1994) | Sand | 0.187 | Borrika (BUF 18) | 60 | −35.1 | 140.1 | Chloride method | 340 | 1800 | Eucalyptus | Grassland |
Cook et al. (1994) | Sand | 0.245 | Borrika (BUF 15) |  | −35.1 | 140.1 | Chloride method | 340 | 1800 | Eucalyptus | Grassland |
Cook et al. (1994) | Sand | 0.245 | Borrika (BEM 35) |  | −34.3 | 139.6 | Chloride method | 340 | 1800 | Eucalyptus | Grassland |
Cook et al. (1994) | Sand | 0.245 | Borrika (BEM 28) |  | −35.1 | 140.1 | Chloride method | 340 | 1800 | Eucalyptus | Grassland |
Cook et al. (1994) | Sand | 0.245 | Borrika (BRC 02) |  | −35.1 | 140.1 | Chloride method | 340 | 1800 | Eucalyptus | Grassland |
Cook et al. (1994) | Sand | 0.245 | Borrika (TATIARA) |  | −35.1 | 140.1 | Chloride method | 340 | 1800 | Eucalyptus | Grassland |
Cook et al. (1994) | Sand | 0.245 | Borrika (BINNUM) |  | −35.1 | 140.1 | Chloride method | 340 | 1800 | Eucalyptus | Grassland |
Cook et al. (1994) | Sand | 0.245 | Borrika (JOANNA) |  | −35.1 | 140.1 | Chloride method | 340 | 1800 | Eucalyptus | Grassland |
Cook et al. (1989) | Loam | 0.216 |  |  | −34.6 | 142.8 | Chloride method and electromagnetic techniques | 312 | 1800 | Eucalyptus | Cropland |
Cook et al. (1989) | Loam | 0.223 |  |  | −34.6 | 143.6 | Chloride method and electromagnetic techniques | 322 | 1800 | Eucalyptus | Cropland |
Cook et al. (1989) | Sand | 0.244 |  |  | −35.1 | 140.1 | Chloride method and electromagnetic techniques | 340 | 1800 | Eucalyptus | Grassland |
Cook et al. (1989) | Sand | 0.245 |  |  | −35.1 | 140.1 | Chloride method and electromagnetic techniques | 340 | 1800 | Eucalyptus | Grassland |
Radford et al. (2009) | Clay | 0.363 | Central Queensland, northern Australia (Baralaba) |  | −24.3 | 149.8 | Chloride method | 632 | 1548 | Woodland | Cropland |
Radford et al. (2009) | Clay | 0.345 | Central Queensland, northern Australia (Capella) |  | −23.1 | 148.1 | Chloride method | 597 | 1638 | Woodland | Cropland |
Radford et al. (2009) | Clay | 0.345 | Central Queensland, northern Australia (Dysart) |  | −22.9 | 148.9 | Chloride method | 580 | 1621 | Woodland | Cropland |
Radford et al. (2009) | Clay | 0.342 | Central Queensland, northern Australia (Gindie) |  | −23.9 | 148.4 | Chloride method | 600 | 1596 | Woodland | Cropland |
Radford et al. (2009) | Clay | 0.379 | Central Queensland, northern Australia (Jambin) |  | −24.3 | 150.4 | Chloride method | 639 | 1548 | Woodland | Cropland |
Radford et al. (2009) | Clay | 0.408 | Central Queensland, northern Australia (Theodore) |  | −24.8 | 150.1 | Chloride method | 700 | 1502 | Woodland | Cropland |
Radford et al. (2009) | Clay | 0.400 | Central Queensland, northern Australia (Wowan) |  | −23.9 | 150.3 | Chloride method | 659 | 1600 | Woodland | Cropland |
Huang and Gallichand (2006) | Loam | 0.273 | Â | Â | 35.3 | 107.8 | Simulation model Simultaneous heat and water transfer (SHAW) | 545 | 810 | Winter wheat | Orchard |
Kesse et al. (2005) | Sand | 0.162 | El Paso | 30 | 32.5 | −105.3 | Simulation | 224 | 2087 | Bare | Shrubs/brush |
Keese et al. (2005) | Sand | 0.276 | CPA | 30 | −32.4 | −104.9 | Simulation | 380 | 2169 | Bare | Shrubs/brush |
Kesse et al. (2005) | Sand | 0.247 | Midland | 30 | −32.5 | −102.5 | 1-D simulation using UNSAT-H | 380 | 2169 | Bare | Shrubs/brush |
Kesse et al. (2005) | Sand | 0.329 | Lubbock | 30 | 34 | −102.5 | 1-D simulation using UNSAT-H | 474 | 2034 | Bare | Crops |
Kesse et al. (2005) | Sand | 0.363 | Carson | 30 | 35 | −102.5 | 1-D simulation using UNSAT-H | 497 | 2096 | Bare | Crops |
Kesse et al. (2005) | Sand | 0.411 | Fisher/Jones | 30 | 33 | −100 | 1-D simulation using UNSAT-H | 620 | 2132 | Bare | Trees |
Kesse et al. (2005) | Sand | 0.491 | Starr | 30 | 26 | −97 | 1-D simulation using UNSAT-H | 671 | 1788 | Bare | Trees |
Kesse et al. (2005) | Sand | 0.540 | Bastrop | 30 | 30 | −97.5 | 1-D simulation using UNSAT-H | 810 | 1732 | Bare | Grasses |
Kesse et al. (2005) | Sand | 0.590 | Parker | 30 | 33.5 | −98 | 1-D simulation using UNSAT-H | 855 | 1819 | Bare | Trees and grasses |
Kesse et al. (2005) | Sand | 0.625 | Hopkins/Rains | 30 | 33.8 | −96 | 1-D simulation using UNSAT-H | 855 | 1819 | Bare | trees and grasses |
Kesse et al. (2005) | Sand | 0.623 | Upshur/Gregg | 30 | 33.5 | −94 | 1-D simulation using UNSAT-H | 855 | 1819 | Bare | Trees and grasses |
Moore et al. (2012) | Sand | 0.365 | T1 | 5 | 28.45 | −99.18 | Chloride method | 604 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | T2 | 5 | 28.45 | −99.18 | Chloride method | 604 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | T3 | 5 | 28.45 | −99.18 | Chloride method | 604 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | T1 | 15 | 28.45 | −99.18 | Chloride method | 604 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | T2 | 15 | 28.45 | −99.18 | Chloride method | 604 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | T3 | 15 | 28.45 | −99.18 | Chloride method | 604 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | Z1 | 30 | 28.43 | −99.23 | Chloride method | 526 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | Z2 | 30 | 28.43 | −99.23 | Chloride method | 526 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | Z3 | 30 | 28.43 | −99.23 | Chloride method | 526 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | Z4 | 20 | 28.43 | −99.23 | Chloride method | 526 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | Z5 | 20 | 28.43 | −99.23 | Chloride method | 526 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | Z6 | 25 | 28.43 | −99.23 | Chloride method | 526 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | Z7 | 30 | 28.43 | −99.23 | Chloride method | 526 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | Z8 | 30 | 28.43 | −99.23 | Chloride method | 526 | 1664 | Woodland | Rangeland |
Moore et al. (2012) | Sand | 0.365 | Z9 | 25 | 28.43 | −99.23 | Chloride method | 526 | 1664 | Woodland | Rangeland |
Leaney et al. (2003) |  | 0.380 | U1 |  | 28.43 | −99.23 | Chloride method | 500 | 1664 | Malle eucalyptus | Crop |
Leaney et al. (2003) |  | 0.340 | U2 |  | −36.5 | 141.3 | Chloride method | 450 | 1664 | Malle eucalyptus | Rangeland |
Leaney et al. (2003) |  | 0.307 | U3 |  | −36.4 | 141.4 | Chloride method | 415 | 1664 | Malle eucalyptus | Rangeland |
Leaney et al. (2003) |  | 0.320 | U4 |  | −36.2 | 141.8 | Chloride method | 430 | 1664 | Malle eucalyptus | Crop |
Leaney et al. (2003) |  | 0.332 | U5 |  | −36.1 | 141.1 | Chloride method | 450 | 1664 | Malle eucalyptus | Crop |
Leaney et al. (2003) |  | 0.310 | U6 |  | −36 | 140.9 | Chloride method | 430 | 1664 | Malle eucalyptus | Crop |
Leaney et al. (2003) |  | 0.300 | U7 |  | −35.5 | 140.8 | Chloride method | 120 | 1664 | Malle eucalyptus | Crop |
Leaney et al. (2003) |  | 0.268 | U8 |  | −35.4 | 140.8 | Chloride method | 380 | 1664 | Malle eucalyptus | Crop |
Leaney et al. (2003) |  | 0.240 | U9 |  | −35 | 140.2 | Chloride method | 340 | 1664 | Malle eucalyptus | Crop |
|  |  |  |  |  | −34.9 | 140.1 | Chloride method |  |  |  |  |