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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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on the basis <strong>of</strong> increasing biomass attainment<br />

under nitrogen limiting conditions: Ambrosia<br />

artemisiifolia, Achillea millefolium, Chenopodium<br />

album, Agropyron repens, Agrostis scabra, Poa<br />

pratensis, Sorghastrum nutans, Schizachyrium<br />

scoparium (= Andropogon scoparius) and Liatrus<br />

aspera. From these data he concluded that early<br />

successional species grew more rapidly and<br />

acquired more nitrogen from nitrogen-poor<br />

soils than late successional species.<br />

Some <strong>of</strong> the perennial pioneer species such<br />

as Ammophila breviligulata may receive some<br />

<strong>of</strong> the nitrogen by their association with diazotrophic<br />

bacteria (Azotobacter) in the rhizosphere<br />

(Ralph 1978; Hassouna and Wareing<br />

1964). Apparently the majority <strong>of</strong> nitrogen<br />

required by A. arenaria may be acquired by<br />

this means (Wahab 1975). However, the rhizosphere<br />

nitrogen fixation in sand dunes has not<br />

been independently confirmed. For example,<br />

Holton (1980) in his studies on Ammophila arenaria<br />

and Elymus mollis could not detect any<br />

nitrogen fixation in sand and root samples and<br />

was unable to culture nitrogen-fixing bacteria<br />

from root and rhizosphere collections. How<br />

important is nitrogen fixation to primary succession<br />

in sand dune systems? Several studies<br />

show that although occasional nitrogen-fixing<br />

plant species may occur in early, mid and late<br />

stages <strong>of</strong> succession, their contribution to the<br />

nutrition <strong>of</strong> other co-occurring plant species<br />

is not significant (Barbour et al. 1985; Lichter<br />

1998), because the number <strong>of</strong> nitrogen-fixing<br />

species occurring along a coast is very small<br />

and distributed irregularly. <strong>The</strong> main reasons<br />

for their absence are high energy costs by the<br />

plant in fixing a molecule <strong>of</strong> nitrogen and a<br />

very high requirement <strong>of</strong> other nutrients,<br />

especially phosphorous (Sprent 1993), which<br />

are normally in short supply during early<br />

stages <strong>of</strong> succession in sand dunes.<br />

Nevertheless, several nitrogen-fixing species,<br />

Myrica gale, M. pennsylvanica, Shepherdia<br />

canadensis, Alnus incana and A. rugosa, do<br />

occur at later stages <strong>of</strong> succession. According<br />

to Lichter (1998) and Olson (1958a) even the<br />

contribution <strong>of</strong> these species to nitrogen<br />

THE SAND DUNE ENVIRONMENT 35<br />

accumulation is negligible and thus the gradual<br />

build up <strong>of</strong> nitrogen in the soil depends on<br />

the life history processes <strong>of</strong> a species (Walker<br />

et al. 1986), acquisition <strong>of</strong> atmospheric inputs<br />

and build up <strong>of</strong> organic matter over time.<br />

<strong>The</strong> acquisition <strong>of</strong> nutrients by dune plants<br />

is also facilitated by their association with<br />

mycorrhizal fungi. <strong>The</strong> primary reason for the<br />

increased uptake <strong>of</strong> macro- and micronu trients<br />

is the exploitation <strong>of</strong> increased soil volume by<br />

extra-matrical mycelium <strong>of</strong> the arbuscular<br />

mycorrhizal (AM) fungi. <strong>The</strong> hyphae are more<br />

efficient than plant roots in the absorption <strong>of</strong><br />

soil nutrients. More details are presented in<br />

Chapter 9.<br />

2.12.2 Phosphorous cycle<br />

<strong>The</strong> second most important nutrient in sand<br />

dunes is phosphorous. Unlike nitrogen, phosphorous<br />

does not occur in the atmosphere as<br />

a gas. <strong>The</strong> primary source <strong>of</strong> phosphorous in<br />

sandy substrates is the weathering <strong>of</strong> min erals<br />

such as apatite (Ca 5(PO 4) 3X where X may be<br />

hydroxide [OH], chlorine [Cl] or flourine [F]).<br />

Since the amount <strong>of</strong> apatite in sand is very low,<br />

coastal sand dunes are deficient in P (Fig. 2.12).<br />

Nevertheless, atmosphere does make a small<br />

contribution to the overall input <strong>of</strong> phosphorous<br />

from aerosol spray from oceans, lakes and<br />

rivers, fine dust particles from volcanic ash,<br />

rocks and soil, material <strong>of</strong> organic origin such<br />

as smoke, ash, fine litter, humus, pollen grains<br />

and combustion <strong>of</strong> fossil fuels. Estimates<br />

<strong>of</strong> total phosphorous input from the atmosphere<br />

range from 0.07 to 1.7 kg ha –1 year –1<br />

(Newman 1995). This input is very small, but<br />

it is extremely important for plants in sand<br />

dune systems with little or no phosphorous at<br />

the start <strong>of</strong> primary succession.<br />

In a sand dune chronosequence along Lake<br />

Michigan, the concentration <strong>of</strong> phosphorous<br />

in the upper mineral soil increased to a<br />

maximum until about 345 years but a drastic<br />

decline occurred from 345- to 485-yearold<br />

dunes (Lichter 1998). At 2375 years <strong>of</strong> age<br />

the P levels were even lower than at 25 years,

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