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The ecology of eelgrass meadows in the Pacific Northwest: A ...

The ecology of eelgrass meadows in the Pacific Northwest: A ...

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Wash<strong>in</strong>gton State Game Dept., pers. comm.,<br />

1982), with spr<strong>in</strong>g counts averag<strong>in</strong>g 47,392<br />

birds (up to 58% oE <strong>the</strong> <strong>Pacific</strong> Flyway<br />

passes through Padilla ~ay). An average<br />

<strong>of</strong> 50,rilBB ducks w<strong>in</strong>ter on Padilla and<br />

nearby Samish Bays (over 6,LMB are div<strong>in</strong>g<br />

ducks: canvasbacks, scaup, go ldeneyes,<br />

buffleheads, and scoters on ~adilla Bay<br />

alone; several <strong>of</strong> <strong>the</strong>se species feed on<br />

<strong>eelgrass</strong> or animals with<strong>in</strong> <strong>the</strong> system).<br />

In nor<strong>the</strong>rn Puget Somld, Sitnenstad et al.<br />

(1979) recorded that <strong>the</strong> pr<strong>in</strong>cipal<br />

w<strong>in</strong>ter<strong>in</strong>g sites for black brant were<br />

Padilla Bay, Samish Ray, Discovery Bay,<br />

and Sequiln Bay. In April up to 18,00U<br />

brant were recorded <strong>in</strong> Siunish Bay, 55,Om<br />

<strong>in</strong> Padilla Bay, and 6,000 <strong>in</strong> Discovery<br />

Bay<br />

At Grays Harbor an estimated 5(21,00U ducks<br />

and 6,000 brant use <strong>the</strong> estuary dur<strong>in</strong>g<br />

w<strong>in</strong>ter (Proctor et al. 1990b). Grays<br />

Harbor also supports more than 150,01dU<br />

shorebirds dur<strong>in</strong>g peak migrations and is<br />

an important l<strong>in</strong>k <strong>in</strong> <strong>the</strong>ir migration (ACOE<br />

1977b). In Willapa Bay, 50,000 black<br />

brant overw<strong>in</strong>ter (proctor et al. 1980b).<br />

Only 1,500-2,2l30 brant overw<strong>in</strong>tered <strong>in</strong><br />

1981-82 (Wash<strong>in</strong>gton State Game Dept.,<br />

pers. comm., 1982). At peak periods<br />

Willapa Bay harbors 200,O(a0 or more<br />

waterfowl. It is known rmw that Willapa<br />

Bay and Humboldt Bay are important<br />

w<strong>in</strong>ter<strong>in</strong>g areas for <strong>the</strong> canvasback duck<br />

(850 w<strong>in</strong>ter <strong>in</strong> Willapa Bay with peak<br />

populations at 1,4II0 to 1,600; Proctor et<br />

dl. 1980a,b). W<strong>in</strong>ter<strong>in</strong>g populations <strong>of</strong><br />

ducks <strong>in</strong> Humboldt Bay are 124,000 with an<br />

additional 35,000 black brant.<br />

In <strong>the</strong> Yaqu<strong>in</strong>a estuary, black brant arrive<br />

<strong>in</strong> late October-ear 1 y November, <strong>in</strong>crease<br />

<strong>in</strong> numbers to 350-525 birds <strong>in</strong> mid-<br />

January, and fur<strong>the</strong>r <strong>in</strong>crease to 780-914<br />

birds <strong>in</strong> late March (R.D. Bayer, pers.<br />

ccmn., 1983).<br />

Tfius, <strong>the</strong>re is a large list <strong>of</strong> birds that<br />

directly eat or are dependent on <strong>eelgrass</strong><br />

and its food webs ee able 14). <strong>The</strong><br />

nutrient and energy flows that <strong>the</strong>se birds<br />

control and drive are emrimus <strong>in</strong> scope.<br />

4.8 TROPHIC RELATIONSHIPS AND GENERAL<br />

mum<br />

As with all <strong>the</strong> world's ecosystems, <strong>the</strong><br />

<strong>eelgrass</strong> system supports both graz<strong>in</strong>g and<br />

detrital food webs. Ow<strong>in</strong>g to <strong>the</strong> high<br />

prductivity <strong>of</strong> eelgrdss and its slough<strong>in</strong>g<br />

<strong>of</strong> leaf material from <strong>the</strong> shoots, a third<br />

pathway <strong>of</strong> energy flow is evident, that <strong>of</strong><br />

leaf and detrital exprt.<br />

Recent work <strong>in</strong> <strong>the</strong> tropics has documented<br />

<strong>the</strong> <strong>in</strong>creas<strong>in</strong>g importance <strong>of</strong> <strong>the</strong> direct:<br />

use <strong>of</strong> leaves and epiphytes (graz<strong>in</strong>g,<br />

herbivory), but <strong>in</strong> seayrasses generally<br />

and <strong>eelgrass</strong> <strong>in</strong> particular, <strong>the</strong> detrital<br />

food webs with<strong>in</strong> <strong>the</strong> <strong>eelgrass</strong> <strong>meadows</strong> are<br />

still <strong>the</strong> primary pathway <strong>of</strong> trophic<br />

energy transfer (Kikuchi 1980).<br />

Very few organisms use <strong>the</strong> fresh <strong>eelgrass</strong><br />

plants <strong>in</strong> <strong>the</strong> <strong>Pacific</strong> <strong>Northwest</strong> as food.<br />

Table 14 lists <strong>the</strong> waterfowl which are<br />

overwhelm<strong>in</strong>gly <strong>the</strong> dom<strong>in</strong>ant grazers on<br />

<strong>eelgrass</strong> <strong>in</strong> <strong>the</strong> region. McRoy and<br />

Helfferich (1980) listed only <strong>the</strong> green<br />

urch<strong>in</strong>, Stronglyvcentrotus drobachiensis,<br />

which consma2 fresh <strong>eelgrass</strong>.<br />

It would be useful to have abundant data<br />

on <strong>the</strong> amount <strong>of</strong> energy or production<br />

which is channeled through direct<br />

herbivory, <strong>the</strong> detritaL E d webs, and <strong>the</strong><br />

export route. Unfortunately, only <strong>the</strong> old<br />

study done by Petersen (1918) <strong>in</strong> Denmark<br />

and <strong>the</strong> relatively recent one conducted by<br />

Thayer et al. (1975b) have documented <strong>the</strong><br />

energy flows quantitatively. Thayer et<br />

al. (1975b) concluded that <strong>the</strong> <strong>eelgrass</strong><br />

system exports to adjacent systems, on <strong>the</strong><br />

basis <strong>of</strong> a net <strong>in</strong>crase <strong>of</strong> sedirnent carbon,<br />

but no direct work was done. <strong>The</strong>y also<br />

calculated that <strong>the</strong> macr<strong>of</strong>auna <strong>in</strong> <strong>the</strong><br />

<strong>eelgrass</strong> bed <strong>in</strong> North Carol<strong>in</strong>a consumed<br />

energy equivalent to 55% <strong>of</strong> <strong>the</strong> net<br />

prduction <strong>of</strong> <strong>eelgrass</strong>, phytoplankton, and<br />

benthic algae <strong>in</strong> <strong>the</strong> bed. 'hey calculated<br />

a gross-growth ecological efficiency <strong>of</strong><br />

12% for <strong>the</strong> macr<strong>of</strong>auna <strong>in</strong> <strong>the</strong> bed and 24%<br />

for <strong>the</strong> fish community, suggest<strong>in</strong>g a<br />

fairly efficient system with a surplus <strong>of</strong><br />

energy to support <strong>the</strong> food webs. <strong>The</strong> high<br />

efficiency for <strong>the</strong> fish, <strong>in</strong> large measure<br />

a result <strong>of</strong> high proportions <strong>of</strong> juveniles<br />

<strong>in</strong> <strong>the</strong> community, suggests that <strong>the</strong><br />

<strong>eelgrass</strong> system provides resident fish<br />

with superior shelter, food, and<br />

protection. <strong>The</strong>se fish probably spend a<br />

relatively small proportion <strong>of</strong> <strong>the</strong>ir<br />

energy cop<strong>in</strong>g with environmental extremes,<br />

search<strong>in</strong>g for food, and escap<strong>in</strong>g from<br />

predators, and can use a relatively large<br />

part <strong>of</strong> <strong>the</strong>ir consumed energy for growth

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