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The Ecology of Tijuana Estuary, California: An Estuarine Profile

The Ecology of Tijuana Estuary, California: An Estuarine Profile

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a Succulent<br />

A conceptual model was developed by Zedler<br />

10<br />

--u- Flood Tidal Flow<br />

and Onuf (1984) to describe estuarine filtering<br />

during the wet and dry seasons <strong>of</strong> nonflood years<br />

8 - --*-Ebb Tidal Flow<br />

and during flood years (Figure 59). Nonflood years<br />

are the most commonly occurring condition. During<br />

these times, the estuary is believed to be a sink for<br />

\ nutrients and sediments coming from both the<br />

m m<br />

watershed and the ocean. It is also a sink for salts<br />

n n<br />

that are brought in by tides and accumulated<br />

through evaporation.<br />

2 - 0 0 0<br />

Z<br />

z z<br />

J<br />

O' M ~ J"N Y J~JL a& s b obr ~ baic v JAN F ~ B M am ~ R We have no data on nutrient inputs during<br />

1977 '---I 978-I<br />

natural flood events at Tiiuana <strong>Estuary</strong>, and can<br />

only speculate that nutrient influxes and<br />

accumulat~on rates are greater during flood than<br />

nonflood years. All studies <strong>of</strong> filtering functions<br />

during flooding came after hydrological<br />

modifications had changed both the availability <strong>of</strong><br />

sediments for transport and the rates and timing <strong>of</strong><br />

streamflows. Onuf's comparisons <strong>of</strong> flood effects<br />

at Mugu Lagoon before and after 1970 indicate<br />

that sedimentation was much less during floods<br />

that preceded watershed development. <strong>The</strong><br />

combined floods <strong>of</strong> 1978 and 1980 filled in the<br />

central bay <strong>of</strong> Mugu Lagoon and decreased low-<br />

R tide volume by 40°/0 (Onuf, In press).<br />

s 6 i f ?,<br />

' 4 - ng ++in" 2<br />

Figure 57. Mean concentrations <strong>of</strong> dissolved organic<br />

carbon for flood and ebb tidal waters <strong>of</strong> (a) the<br />

succulent-dominated and (b) cordgrass-succulent<br />

study sites <strong>of</strong> Winfield (1980). Reprinted with<br />

permission from Winfield (1 980).<br />

high, it is unwise to set a percentage for materials<br />

lost from the marsh to adjacent tidal creeks.<br />

Suffice it to say that, from these early data, most <strong>of</strong><br />

the marsh plant production appears to be used<br />

within the marsh.<br />

4.5.4 Temporal Variability in Filtering Functions<br />

<strong>The</strong>re is little information on year-to-year<br />

differences in nutrient uptake rates, sediment<br />

accretion, and peat formation. Limited studies <strong>of</strong><br />

peat accumulation (Scott 1976; Mudle and Byrne<br />

1980) show that marsh elevations have increased<br />

through geologic time, and comparisons <strong>of</strong><br />

elevations before and after flooding (Zedler 1983b)<br />

document short-term accretion. Not much can be<br />

satd about the processes that reverse these<br />

"filtering" functions, either. No measurements have<br />

been made <strong>of</strong> erosion, other than what is obvious<br />

from aerial photos (Chapter 2). Overall, <strong>Tijuana</strong><br />

<strong>Estuary</strong> is accumulating sediments within the<br />

channels and losing area due to shoreline retreat,<br />

but the processes appear to be more catastrophic<br />

than chronic.<br />

Disturbances wlthln the watershed <strong>of</strong> <strong>Tijuana</strong><br />

<strong>Estuary</strong> have destabilized slopes and made<br />

available large volumes <strong>of</strong> sediment, just as in the<br />

watershed <strong>of</strong> Mugu Lagoon. Unlike Mugu Lagoon,<br />

<strong>Tijuana</strong> <strong>Estuary</strong> is somewhat protected from<br />

sed~ment deposrtion by dams that regulate 78% <strong>of</strong><br />

the watershed. Still, agricultural and urban<br />

developments below Rodriguez Dam disturb soils<br />

that can be mobilized by flooding Aerial photos <strong>of</strong><br />

the 1980 flood show major sediment plumes<br />

flowing out <strong>of</strong> the mouth <strong>of</strong> <strong>Tijuana</strong> <strong>Estuary</strong>. Only a<br />

small portion <strong>of</strong> the sediment was deposited within<br />

the wetland.<br />

Because the bulk <strong>of</strong> the filtering process occurs<br />

as sedimentatlon during catastrophic events, it is<br />

not clear how important the vascular plants are in<br />

controlling the processes <strong>of</strong> accretion and erosion.<br />

In coastal systems worldwide, there are attempts to<br />

stabilize shorelrnes by maintaining good cover <strong>of</strong><br />

beach grasses and cordgrass. At <strong>Tijuana</strong> <strong>Estuary</strong>,<br />

the ~mportance <strong>of</strong> beach vegetation in reducing<br />

sed~ment mobilization is clear, but the role <strong>of</strong><br />

cordgrass is not. Cordgrass does not occur In the<br />

path <strong>of</strong> the rlver; thus, ~t cannot reduce erosion<br />

along the river banks. Some areas <strong>of</strong> pickleweed<br />

~n the estuary and even some woody vegetation<br />

upstream were scoured out by the 1980 flood.<br />

Cordgrass may be effectlve in increasing<br />

sedimentatlon within the salt marsh. Whether this<br />

IS beneficial or detrimental to maintenance <strong>of</strong><br />

wetland habitats depends on the comblned rates <strong>of</strong><br />

accretion and sea level rise.

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