Abstract

Author(s): Hutton, Paul H.; Roy, Sujoy B. | Abstract: We evaluated two historically important data sets to characterize the San Francisco Estuary’s salinity regime before the State of California began systematic data collection in the early 1920s. One set documents barge travel along the Sacramento and San Joaquin rivers to obtain water of adequate quality for local industry; a second set documents Delta inflow used to compute antecedent outflow. The barge travel distance reported over 2 decades (1908–1929) was well explained by flow–salinity modeling, indicating internal consistency in these measurements. However, absolute salinity intrusion estimated through the barge travel data is systematically lower than suggested by contemporaneous water-quality measurements available since 1921. Through integration of these data sets, our work showed substantial similarities between 1908–1921 and the subsequent period before construction of Shasta Dam (1922–1944). Our analysis reveals an apparent shift in the estuary’s salinity regime, with lesser salinity intrusion occurring in pre-1919 summer and fall months as a result of higher summer Delta outflow; this shift may be related to lower storage and irrigation diversions as well as a preponderance of wet years with higher summer runoff in the pre–1919 period. We found seasonal patterns of wet year salinity intrusion to be comparable over the full study period (1908–1944), indicating that the relative effect of upstream water management is minimal when flows are high, consistent with findings reported in later periods. The barge and flow data provide qualitative insights on early 20th century conditions, when limited data are available. Post–1920 hydrology and salinity data are preferable for quantitative analyses because of better documentation associated with collection and analysis, and sustained reporting over several decades. This work provides a foundation for future efforts to characterize the hydrologic and hydrodynamic changes that occurred in the system between the 1850s (i.e., natural or pre-development conditions) and the 1920s.

Highlights

  • The settlement and economic development of California after the Gold Rush era of the 1850s was closely associated with large-scale hydrologic modification, especially in the San Francisco Estuary and its upstream watershed

  • Changes over the following decades included conversion of land use from natural vegetation to agriculture, removal of riparian vegetation, levee construction as well as stream channelization and dredging to aid navigation and flood control, mining of hillsides with water jets, extensive water diversions from streams to support growing demands for irrigated agriculture and urban uses, and early development of in-stream storage facilities (CDPW 1931; Kelley 1989; Hundley 2001; Lund et al 2010). These changes — which dramatically affected the hydrology, geomorphology, water quality, and ecosystem of the estuary and its watershed — were followed, beginning in the 1940s, by further hydrologic alterations associated with the federal Central Valley Project (CVP) and California’s State Water Project (SWP)

  • Routine salinity sampling along the estuarine gradient was initiated during this time by the California Department of Public Works (CDPW), the predecessor to California Department of Water Resources (CDWR) (CDPW 1931)

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Summary

Introduction

The settlement and economic development of California after the Gold Rush era of the 1850s was closely associated with large-scale hydrologic modification, especially in the San Francisco Estuary (estuary) and its upstream watershed. Changes over the following decades included conversion of land use from natural vegetation to agriculture, removal of riparian vegetation, levee construction as well as stream channelization and dredging to aid navigation and flood control, mining of hillsides with water jets (termed hydraulic mining), extensive water diversions from streams to support growing demands for irrigated agriculture and urban uses, and early development of in-stream storage facilities (CDPW 1931; Kelley 1989; Hundley 2001; Lund et al 2010) These changes — which dramatically affected the hydrology, geomorphology, water quality, and ecosystem of the estuary and its watershed — were followed, beginning in the 1940s, by further hydrologic alterations associated with the federal Central Valley Project (CVP) and California’s State Water Project (SWP). Contemporary flow and salinity conditions in the Delta are influenced by these changes as well as by evolving salinity regulations that have been applied since the 1970s (see Hutton et al 2015 for discussion)

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