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Principles of terrestrial ecosystem ecology.pdf

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from one another in their capacity to act as<br />

sinks for incoming materials, due to variation in<br />

basin geometry, sediment input, and tidal interactions.<br />

The stability <strong>of</strong> the landscape on the<br />

Mississippi River Delta, for example, depends<br />

on regular delivery <strong>of</strong> sediments from upstream<br />

to replace soils removed by tidal erosion. Channels,<br />

levees, and other engineering solutions<br />

to flood control and water management may<br />

reduce the probability <strong>of</strong> flooding but greatly<br />

augment the land loss to coastal erosion<br />

(Costanza et al. 1990). Many estuaries, including<br />

the Gulf <strong>of</strong> Mexico near the entrance <strong>of</strong> the<br />

Mississippi River, are becoming saturated by<br />

nutrient enrichment within their watersheds,<br />

resulting in harmful algal blooms, loss <strong>of</strong> seagrass,<br />

and increasing frequency <strong>of</strong> anoxia or<br />

hypoxia and related fish kills (Mitsch et al.<br />

2001).<br />

Atmospheric Transfers<br />

Atmospheric transport <strong>of</strong> gases and particles<br />

links <strong>ecosystem</strong>s over large distances and<br />

coarse spatial scales. Gases emitted from<br />

managed or natural <strong>ecosystem</strong>s are processed<br />

Fertilizer N<br />

Source region Sink region<br />

Fossil fuel and<br />

biomass combustion<br />

Crop<br />

Trace<br />

gases<br />

Patch Interactions on the Landscape 317<br />

in the atmosphere and can be transported for<br />

distances ranging from kilometers to the globe.<br />

Particulates from biomass burning, wind-blown<br />

dust, sea spray, and anthropogenic sources can<br />

also be carried through the atmosphere from<br />

one <strong>ecosystem</strong> to another. Once deposited, they<br />

can alter the functioning <strong>of</strong> the recipient<br />

<strong>ecosystem</strong>s (Fig. 14.8), just as with topographically<br />

controlled transfers.<br />

In areas downwind <strong>of</strong> agriculture, ammonia<br />

gas (NH3) and nitric oxides (NOx) can represent<br />

a significant fraction <strong>of</strong> nitrogen deposition.<br />

Dutch heathlands, for example, receive<br />

10-fold more nitrogen deposition than would<br />

occur naturally. The magnitude <strong>of</strong> these inputs<br />

is similar to the quantity <strong>of</strong> nitrogen that annually<br />

cycles through vegetation, greatly increasing<br />

the openness <strong>of</strong> the nitrogen cycle. Areas<br />

downwind <strong>of</strong> industry and fossil fuel combustion<br />

receive nitrogen largely as NOx. Sulfur<br />

gases, including sulfur dioxide (SO2), are also<br />

produced by fossil fuel combustion, although<br />

improved regulations have reduced these emissions<br />

and deposition relative to NOx.<br />

The large nitrogen inputs to <strong>ecosystem</strong>s have<br />

important consequences for NPP, nutrient<br />

Deposition<br />

Trace<br />

gases<br />

Leaching Leaching<br />

Figure 14.8. Atmospheric transfers <strong>of</strong> gases, solutions, and particulates among <strong>ecosystem</strong>s. Inputs come from<br />

fossil fuel and biomass combustion and from trace gases originating from natural and managed <strong>ecosystem</strong>s.

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