The Inyo/Los Angeles Water Agreement established procedures to determine
which LADWP pumping wells can be operated based on soil water and vegetation
measurements. Staff from the Water Department routinely monitors depth to
groundwater and soil water content at 25 sites in wellfields and eight sites
in control areas. Data from 22 wellfield sites visited each month are used
to determine the operational status (On or Off) of nearby pumping wells. In
October 2002, nine sites were in On-status. Three sites with low plant cover
entered On-status following November storms and one site entered On-status
in March due to water table recovery and precipitation.
The purpose for the On/Off procedures is to manage pumping to protect
plant communities that require periodic connection to the water table for
long-term survival. Generally, the sites with On-status have wet soil and
shallow water tables, and the Off-status sites have dry soil and deep water
tables. The On/Off determination is affected by several other factors,
however, and sometimes On-status sites are those with a deep water table and
low plant cover. Conversely, a site with adequate water table depth may be
in Off-status if the water table occurs just below the root zone and plant
cover is high. These inconsistencies contradict the assumption that
operating pumps in On-status will not adversely affect vegetation near the
monitoring sites, but operating wells in Off-status will.
We determine which monitoring sites are connected with the water table
to give a clearer picture of the conditions underground that are affected by
pumping. We rely on soil water and groundwater data because the water table
depth necessary to provide water to the plant roots depends on the soil
characteristics as well as water table depth. For example, the capillary
rise above the water table in a silty soil is much greater than in a sandy
soil. At the same water table depth, the plants may have access to
groundwater if the soil is silty, but not if it is sandy. How well plant
roots can take up groundwater also depends on the type of vegetation. In
similar soils, a shallower water table is necessary to supply groundwater to
grasses than shrubs because of the shallower roots of the grasses. For
management purposes, grass-dominated monitoring sites are assigned a root
zone of 2 meters; shrub sites are assigned a root zone of 4 meters.
The wellfield monitoring sites were grouped into three categories to
summarize the connection between the root zone and the water table. Brief
descriptions of the three categories are given below.
The relatively low pumping and high runoff from 1995 to 1998 caused the water table and soil water recovery to increase at most monitoring sites from the decline induced by drought and large amounts of pumping in the late 1980s. Since 1999, however, the water table stopped rising or began to decline at most sites because of lower runoff, increased pumping, or because water tables approached shallow depths similar to pre-drought levels. Consequently, the number of sites where soil water responds to water table fluctuations has decreased. As of April 2003, the water table was supplying water to the root zone at twelve monitoring sites located in wellfields (Figure 5). This compares to about 20 sites with groundwater in the root zone in 2000. Soil water at slightly more than half of the sites (13) did not increase at depth after plant transpiration ceased in the fall of 2002 and/or did not respond to water table increases over the following winter suggesting that the water table and root zone are disconnected.
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