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The Ecology of Tijuana Estuary, California: An Estuarine Profile

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and height were lower than ever before recorded.<br />

<strong>The</strong> delayed reaction <strong>of</strong> cordgrass tsl<br />

measurements was due to the longevity <strong>of</strong> the<br />

plant. Individual stems live 1.5-2.0 years, and the<br />

1984 measurements included stems with some live<br />

materlal from the previous growing season. By<br />

1985, there were few plants from the previous year<br />

and few individuals from 1985, even though tidal<br />

flushing had been reinstated throughout the entire<br />

growing season.<br />

To interpret these variations in cordgrass<br />

growth requires consideration <strong>of</strong> the effects <strong>of</strong><br />

hydrological change on pickleweed, because<br />

pickleweed is the competitive dominant (Zedler<br />

1982; Covin 1984) and its distribution overlaps<br />

with cordgrass throughout most <strong>of</strong> the lower marsh.<br />

Years <strong>of</strong> high pickleweed cover were 1979, 1981,<br />

and 1984-85 (Table 26). <strong>The</strong>se same years had<br />

low cordgrass biomass. Cordgrass tsl can be high<br />

when two conditions are met. First, there must be<br />

appropriate salinity, nutrients, and soil moisture;<br />

and second, there must be reduced competition<br />

from pickleweed. <strong>The</strong> latter condition appears to<br />

be associated with reduced drainage, that is.<br />

increased inundation. Several experimental tests<br />

<strong>of</strong> these hypotheses have been initiated.<br />

5.4.1 Hydrology and Salinity Experiments<br />

Figure 66. Changes in average height <strong>of</strong> cordgrass.<br />

Means are based on the total number <strong>of</strong> stems<br />

measured each year.<br />

<strong>An</strong> experimental field study was initiated in<br />

1984 to determine how coastal wetlands would<br />

respond to increased streamflow caused by treated<br />

wastewater. <strong>The</strong> data provide a test <strong>of</strong> the above<br />

hypotheses concerning cordgrass responses to<br />

salinity reductions at different times <strong>of</strong> the year. A<br />

brief summary and pertinent findings follow from<br />

the work <strong>of</strong> Beezley and Beare (SDSU, unpubl<br />

data).<br />

,,.,.-<br />

. r.,ir)<br />

3 7av I :?(>L ? '384<br />

Year<br />

Figure 67. Changes in the maximurn height <strong>of</strong> Figure 68. Changes in the density <strong>of</strong> cordgrass stems.<br />

cordgrass. Means are from the number <strong>of</strong> quadrats in Means are from the number <strong>of</strong> quadrats in which<br />

which cordgrass was present each year (Figure 621. cordgrass was present each year (Figure 62).

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