California Water Science Center
Historically, the Sacramento—San Joaquin Delta (Delta) in California was a vast inland freshwater wetland where organic soils over 50 feet deep formed over several millennia. Beginning in the late 1800’s, levees were constructed and pumps were used to drain the area for agricultural use. Draining these lands has led to land-surface subsidence A dropping of the land surface.
While land-surface loss can be due to dewatering, groundwater pumping, or soil compaction, in the Delta the dominant cause is loss of the organic-rich peat soils due to microbial degradation. Put simply, microbial activity — which is enhanced under drained (oxygen rich) conditions compared to flooded (oxygen poor) conditions — converts the organic rich soil to carbon dioxide gas (CO2). to more than 20 feet below sea level in some areas, primarily due to oxidative loss of the organic rich soils. Because the Delta supplies drinking water for over 23 million Californians, protecting both water supply and water quality in this region is of great importance.
Map of the Sacramento-San Joaquin Delta. Click to Enlarge.
Rivers, wetlands, and agricultural operations supply natural organic material to the Sacramento-San Joaquin Delta (Delta) and the San Francisco Estuary. This natural organic matter provides many ecosystem benefits, but it also adversely affects drinking water. This occurs because during drinking water treatment, chlorine added for purposes of pathogen control dissolved organic carbon (DOC) in the water to form carcinogenic and mutagenic disinfection by-products (DBPs). Concentrations of these compounds in tap water are regulated by the Environmental Protection Agency.
Because much of the land in the Delta is below sea level, drainage water must be continuously pumped into adjacent Delta channels to prevent these areas from flooding. This drainage water typically contains high concentrations of DOC and DBP precursors because they have passed over and through high organic matter peat soils (Fujii et al. 1998, Fleck et al. 2007). Drainage water from Delta peat islands has been shown to represent a significant source of these constituents of concern to drinking water diverted from the Delta (Kraus et al. 2009). Management actions that reduce the export of these constituents from subsided islands will improve water quality in the Delta.
Land-surface subsidence and the resulting dependence on levees threaten water supply, capital investments, and public safety in the Delta. This situation is becoming less sustainable with continued subsidence and rising sea level.
As land surface elevations decrease, costs for levee maintenance and repair increase, as do the risks of catastrophic levee failure. Currently 98 percent of the Delta is below sea-level (Knowles 2010). In addition to immediate loss of life and property associated with levee failure, saltwater intrusion into this freshwater system could result and halt water exports for an extended period of time (Mount and Twiss 2005). Management actions that reduce, or better yet reverse, subsidence in the Delta would reduce these costs and risks.
The primary goals of this project are to assess the feasibility of the following:
This low-intensity chemical-dosing (LICD) method is anticipated to remove considerable amounts of DOC and DBP precursors from island drainage water, thereby significantly reducing inputs of these constituents to the Delta. Accumulation of the flocculated material in wetlands, along with sequestration of wetland plant material, is expected to increase land-surface elevations. The project hypothesis is that the combination of coagulation and biotic wetland processes can improve water quality and reverse subsidence beyond that achievable by either technology alone.
This project combines laboratory and field studies to assess the feasibility and ecosystem effects of LICD. Specific study objectives include the following:
FEASIBILITY—Determine costs associated with constructing and maintaining a coagulation system.
This project will include both laboratory and field based studies. Laboratory studies will assess the efficacy of coagulant type and dosing rates for removing DOC, DBP precursors, and other constituents of concern (e.g. mercury) from island drainage water, as well as assess characteristics and stability of the flocculated material.
Construction of a replicated field experiment located on Twitchell Island will allow us to determine the effects of a coagulation treatment-wetland system on water quality. The experimental design includes three coagulation treatments—an iron-based coagulant (iron sulfate), an aluminum-based coagulant (polyaluminum chloride), and a control (no coagulant addition). There are three replicates of each treatment for a total of nine wetland cells. This system is expected to run from Fall 2011 to Fall 2013. The effects of the treatment-wetland systems will be assessed by monitoring water quality, sediment accretion, plant production, and aquatic organism health.
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