Evaluating the Potential of Well Profiling Technology to Limit Irrigation Water Salinity in California Vineyards

Grape growers in some regions of California are confronting problems with soil salinity. Improving irrigation water quality at the source well offers a potential solution to mitigate soil salinity issues in vineyards. Here, we utilized tracer-pulse technology and chemical analysis to assess flow and constituent contributions at various points throughout the depth profiles of three wells with known salinity problems. At the surface, all three wells had several chemical constituents measuring at concentrations higher than the recommended threshold for grapevines. Theoretical well manipulation effects were calculated to evaluate whether blocking inflow at each layer of each well's depth profile would improve overall water quality at the surface. The profiling technology effectively measured variation in flow and chemical contributions along each profile. As no strong chemical hotspots were detected and the distributions were relatively uniform/symmetric across each of the depth profiles, the theoretical well manipulation offered little improvement in overall well water quality without detrimental effects on volume pumping capacity. For example, in one well a manipulation inserted at 73- to 113-m below ground surface would reduce the overall concentration of several constituents of concern, but would be accompanied by a 41% reduction in well flow. While a well manipulation would have minimal effect for the three wells assessed in this study, this method could be an effective means of improving irrigation water quality for wells with stronger asymmetrical patterns of constituent contributions.

[1]  Harry I. Nightingale,et al.  Well‐Water Quality Changes Correlated with Well Pumping Time and Aquifer Parameters—Fresno, Californiaa , 1980 .

[2]  P. Kriedemann,et al.  An Analysis of Photosynthetic Response to Salt Treatment in Vitis vinifera , 1981 .

[3]  Pacific Northwest Cooperative Extension,et al.  Managing irrigation water quality for crop production in the Pacific Northwest , 2007 .

[4]  T. Charbaji,et al.  Effect of sodium chloride salinity on cation equilibria in grapevine , 1993 .

[5]  R. Ayers,et al.  Water quality for agriculture , 1976 .

[6]  L. Eccles,et al.  Abatement of Nitrate Pollution in a Public-Supply Well by Analysis of Hydrologic Characteristicsa , 1976 .

[7]  K. Chartzoulakis,et al.  Response of Sultana vines (V. vinifera L.) on six rootstocks to NaCl salinity exposure and recovery , 2001 .

[8]  J. Tisdall,et al.  A diminished capacity for chloride exclusion by grapevine rootstocks following long-term saline irrigation in an inland versus a coastal region of Australia. , 2006 .

[9]  G. J. Beke,et al.  Long‐Term Quality of Shallow Ground Water at Irrigated Sites , 1993 .

[10]  K. Mengel,et al.  Bicarbonate, the most important factor inducing iron chlorosis in vine grapes on calcareous soil , 1984, Plant and Soil.

[11]  M. A. Anderson,et al.  Vineyard nutrient needs vary with rootstocks and soils , 2008 .

[12]  S. Lesch,et al.  Effect of SAR on water infiltration under a sequential rain-irrigation management system , 2006 .

[13]  U. Shani,et al.  Long-term Response of Grapevines to Salinity: Osmotic Effects and Ion Toxicity , 2005, American Journal of Enology and Viticulture.

[14]  P. Hudak Sodium adsorption ratios and salinity levels in nine texas aquifers: implications for irrigated agriculture , 2001 .