MILLER, DALE, BRUSH, VICUNA, KADIR, DOGRUL, AND CHUNG
<br />coincident with the Little Ice Age cooling period.
<br />Samples from sediments, tree rings, and tree stumps,
<br />combined with isotope dating analysis have been used
<br />to reconstruct these naturally occurring droughts
<br />that lasted 50 to more than 100 years (Stine, 1994;
<br />Herweijer et al., 2006; Cook et al., 2007). Indeed, two
<br />epic drought periods, one lasting from approximately
<br />900 -1100, and the second lasting from about 1200-
<br />1350, contributed to the decline and disappearance of
<br />the Anasazi people, a culture that relied on irrigated
<br />agriculture to support its population. Drought is also
<br />seen as a contributing factor in the failure of Euro-
<br />pean colonies in South Carolina and North Carolina
<br />in the 1500s. More recently, four droughts in the wes-
<br />tern U.S. centered on AD 1710, 1770, 1850, and 1930
<br />have been associated with the Pacific Decadal Oscilla-
<br />tion (PDO), and indicate drought recurrence intervals
<br />of 60 -80 years (Benson et al., 2003) and a linkage to
<br />large -scale climatic phenomena.
<br />During the last 150 years, California has been in a
<br />slightly above average wet regime, with an annual
<br />average precipitation of 58 cm (23 inches), and at
<br />least 11 significant drought periods (Ingram et al.,
<br />1996; Cook et al., 2004). At the same time, California
<br />Central Valley agriculture has expanded over most of
<br />the Valley floor, and includes a system of managed
<br />irrigation and water conveyance that has assumed
<br />climatically stationary conditions for conveyance sys-
<br />tem development and planning. The 1929 -1934
<br />drought has traditionally been the benchmark event
<br />used for designing storage capacity and yield of large
<br />California reservoirs. The stationarity principle may
<br />no longer be valid, as substantial anthropogenic
<br />changes in Earth's climate are altering the means
<br />and extremes of precipitation, evapotranspiration,
<br />and rates of discharge to rivers (Milly et al., 2008).
<br />Changes in the temperature regime in California
<br />associated with projected future climate are expected
<br />to result in reduced winter snowpack and increased
<br />winter runoff (Miller et al., 1999; Hayhoe et al., 2004;
<br />Maurer and Duffy, 2005). In addition, the population
<br />of California's Central Valley has increased from less
<br />than 3 million people in 1970 to more than 6 million
<br />in 2002, and is projected to increase to 15 million peo-
<br />ple by 2050 (U.S. Bureau of the Census 1982; Califor-
<br />nia Department of Finance 2007). Since the 1970s, as
<br />the urban area of the Central Valley has increased,
<br />agricultural acreage has remained relatively constant
<br />by expanding into previously uncultivated land. The
<br />increase in population coupled with constant agricul-
<br />tural acreage has resulted in steadily increasing
<br />water demands. Approximately 35% of the water
<br />demand in the Central Valley is currently met with
<br />ground water (California Department of Water
<br />Resources 2003), with pumping rates increasing
<br />in years of reduced surface water availability. Flow
<br />deficits associated with future climate scenarios, cou-
<br />pled with present and future levels of water demand,
<br />may inflict significant stress on Central Valley aqui-
<br />fers. In light of these challenges, the California
<br />Department of Water Resources (CDWR) and other
<br />water agencies have begun to evaluate new
<br />approaches for incorporating the changing climate
<br />into water resources planning and management
<br />(CDWR, 2006; Anderson et al., 2008).
<br />The goals of this study are to quantify the impacts
<br />of long -term hydrologic droughts — a first -order
<br />approximation of an analogue for climate change
<br />related snowpack reduction — on water storage, and
<br />to illustrate the potential for surface and subsurface
<br />storage to limit the adverse impacts of drought and
<br />snowpack reduction on water supply and hydropower
<br />generation. This includes how ground -water pumping
<br />compensates for reductions in surface water inflow;
<br />the extent to which the water table is reduced; and
<br />how, when, and if this system recovers or reaches a
<br />new equilibrium. In the next section, we provide
<br />details on our approach for simulating persistent
<br />droughts in the California Central Valley. This is
<br />followed by the results and discussion section, then
<br />our summary and conclusions.
<br />APPROACH
<br />This analysis of the impacts of sustained droughts
<br />in the California Central Valley is based on a series
<br />of specified reductions in net surface water inflows
<br />observed during the 1923 -1972 period. The reductions
<br />considered in the study represent a 30% (below aver-
<br />age), 50% (dry), and 70% (critically dry) effective
<br />reduction for periods ranging from 10 to 60 years,
<br />and were applied to the CDWR's California Central
<br />Valley Ground water- Surface Water Simulation Model
<br />(C2VSIM). The methodology used here is part of a
<br />series of analyses that allow for the decomposition
<br />and response term by term, allowing for a reduction -
<br />ist evaluation of the impacts of decreases in net sur-
<br />face flow from reservoirs and Central Valley
<br />precipitation. Previous studies of California's future
<br />water supply were based on downscaled climate
<br />model projections with hydrologic model simulations
<br />and permutations of the 1922 -1993 unimpaired
<br />streamflows (Miller et al., 2003) with an operating
<br />criterion of maximizing statewide water supply net
<br />benefits (e.g., Lund et al., 2003; Zhu et al., 2005;
<br />Tanaka et al., 2006; Medellin - Azuara et al., 2008).
<br />However, these studies are unable to pin down the
<br />term -by -term isolated response to droughts, present
<br />day or future. With that in mind, it was deemed
<br />JAWRA 858 JOURNAL OF THE AMERICAN WATER RESOURCES ASSOCIATION
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