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The Biology of Coastal Sand Dunes M. Anwar Maun - Inecol

The Biology of Coastal Sand Dunes M. Anwar Maun - Inecol

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54 BIOLOGY OF COASTAL SAND DUNES<br />

<strong>of</strong> the dune system. Seed size is an important<br />

factor that is related to whether a species<br />

would possess a transient or a persistent<br />

seed bank. Usually species with a persistent<br />

seed bank have small seeds (Thompson and<br />

Grime 1979).<br />

4.2.1 Transient seed bank<br />

Many species <strong>of</strong> the foredunes possess a transient<br />

seed bank and can only survive in habitats<br />

with recurrent sand movement, high wind<br />

velocities and full sunlight. <strong>The</strong>y are opportunistic,<br />

are dispersed by wind and water,<br />

may possess both vegetative and reproductive<br />

means <strong>of</strong> regeneration and require regular disturbance<br />

for survival. <strong>The</strong> energy required to<br />

develop adaptations for persistence <strong>of</strong> the seed<br />

bank will be too costly and will not increase<br />

their fitness. Based on observations over the<br />

last 30 years on the Pinery sand dunes, the persistence<br />

<strong>of</strong> fugitive annuals and monocarpic<br />

perennials on the strand is dependent on prolific<br />

and reliable seed production and effective<br />

dispersal. Seed production in these species<br />

has fluctuated over time but has never failed<br />

in these years. <strong>The</strong>se plants are resilient and<br />

capable <strong>of</strong> high phenotypic plasticity in size<br />

which varies depending on the microhabitat<br />

<strong>of</strong> their occurrence on the shoreline. On beach<br />

sections used heavily for recreation by people,<br />

most <strong>of</strong> the seedlings are killed by trampling,<br />

but in early spring or next summer, the driftline<br />

is covered yet again with a large number<br />

<strong>of</strong> seedlings from seeds that have immigrated<br />

from nearby undisturbed beaches.<br />

Planisek and Pippen (1984) examined sand<br />

samples (7.5 cm diameter × 11 cm deep) from<br />

the beach, foredunes, slack and dune forest in<br />

November 1981 along the eastern shore <strong>of</strong><br />

Lake Michigan. <strong>The</strong> sifting <strong>of</strong> soil samples<br />

yielded no seeds from the beach and foredune<br />

which is rather surprising because Cakile edentula<br />

(a common plant on the beach) must have<br />

dispersed its fruits by November. <strong>The</strong> slack<br />

and forest contained 0.74 and 3.2 seeds per<br />

sample, respectively, but none <strong>of</strong> these seeds<br />

was viable. It was concluded that coastal foredunes<br />

do not have a seed bank primarily<br />

because <strong>of</strong> substrate instability. Similarly,<br />

Looney and Gibson (1995) showed that in four<br />

habitats, the frequently disturbed beaches<br />

(extensive sand movement, salt spray), unvegetated<br />

sandy areas, early successional dredge<br />

spoils and the strand <strong>of</strong> a coastal barrier island<br />

<strong>of</strong> Florida, the seed banks <strong>of</strong> Cakile constricta,<br />

Oenothera humifusa, Iva imbricata, Hydrocotyle<br />

bonariensis and Heterotheca subaxillaris were<br />

transient and poorly developed. <strong>The</strong> dune<br />

annuals, Cerastium atrovirens (Mack 1976),<br />

Vulpia fasciculata and V. ciliata (Carey and<br />

Watkinson 1993) at Aberffraw, North Wales,<br />

also did not have any carry-over <strong>of</strong> seeds from<br />

one year to the next. This is rather surprising<br />

because annuals or biennials are more likely<br />

to have persistent seed banks in habitats with<br />

recurrent disturbance (Thompson et al. 1998).<br />

Baptista and Shumway (1998) determined<br />

the seed bank composition <strong>of</strong> sand dunes with<br />

different disturbance histories at Cape Cod<br />

National Seashore and found that both the<br />

density <strong>of</strong> viable seeds in sand samples and<br />

species diversity were very low (Table 4.1). <strong>The</strong><br />

seeds exhibited a clumped distribution, probably<br />

because <strong>of</strong> (i) accumulation <strong>of</strong> seeds in<br />

depressions following wind dispersal, and<br />

(ii) burial <strong>of</strong> complete infructescences <strong>of</strong> plants<br />

before the release <strong>of</strong> their seeds. A similar<br />

seed bank pattern was also observed in desert<br />

dunes by Kemp (1989), who concluded that the<br />

frequency <strong>of</strong> seed distribution was kurtotic,<br />

with a large number <strong>of</strong> seeds in some samples<br />

and a few or none in most and that the abundance<br />

<strong>of</strong> a species was not a good predictor <strong>of</strong><br />

the abundance <strong>of</strong> its seeds in the seed bank.<br />

Seed bank dynamics <strong>of</strong> Cirsium pitcheri, an<br />

endangered species in Canada and federally<br />

threatened species in the United States <strong>of</strong><br />

America, was examined by Rowland and<br />

<strong>Maun</strong> (2001). <strong>The</strong>y removed 700 cores <strong>of</strong> sand<br />

each 2.5–5.0 cm diameter × 35 cm deep located<br />

on transects perpendicular to the beach and<br />

extending to the leeward side <strong>of</strong> the second<br />

dune ridge. <strong>The</strong>y then sifted the sand to

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