Principles of terrestrial ecosystem ecology.pdf
Principles of terrestrial ecosystem ecology.pdf
Principles of terrestrial ecosystem ecology.pdf
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High albedo<br />
High RH<br />
-30% Precipitation<br />
Dry air<br />
subsides<br />
Air m ovement<br />
Figure 14.10. Effects on regional climate <strong>of</strong> conversion<br />
from heathland to barley croplands in southwestern<br />
Australia (Chambers 1998). The heathland<br />
absorbs more radiation (low albedo) and transmits a<br />
larger proportion <strong>of</strong> this energy to the atmosphere<br />
as sensible heat than does adjacent croplands. This<br />
causes air to rise over the heathland and draws in<br />
monoxide and nonmethane hydrocarbons react<br />
in the troposphere to produce ozone and other<br />
atmospheric pollutants that can affect downwind<br />
<strong>ecosystem</strong>s (see Chapter 2). Nitrogen is<br />
also released in various oxidation states, including<br />
nitrogen oxides (NO and NO2, together<br />
known as NOx) and ammonia. The proportional<br />
release <strong>of</strong> these forms also depends on<br />
the intensity <strong>of</strong> the burn, with NOx typically<br />
accounting for most <strong>of</strong> the emissions. Sulfurcontaining<br />
gases; organic soot and other aerosol<br />
particles; elemental carbon; and many trace<br />
species <strong>of</strong> carbon, nitrogen, and sulfur also have<br />
important regional and global effects. Satellite<br />
and aircraft data show that these gases and<br />
aerosols in biomass-burning plumes can be<br />
transported long distances.<br />
Windblown particles <strong>of</strong> natural and anthropogenic<br />
origins link <strong>ecosystem</strong>s on a landscape.<br />
The role <strong>of</strong> the atmosphere as a transport<br />
pathway among <strong>ecosystem</strong>s differs among elements.<br />
For some base cations (Ca 2+ ,Mg 2+ ,Na + ,<br />
and K + ) and for phosphorus, dust transport is<br />
the major atmospheric link among <strong>ecosystem</strong>s.<br />
At the local to regional scales, dust from roads<br />
or rivers can alter soil pH and other soil<br />
Moist<br />
air<br />
rises<br />
Crop Natural vegetation<br />
Patch Interactions on the Landscape 319<br />
+10% Precipitation<br />
Low albedo<br />
High roughness<br />
High sensible heat<br />
High air temperature<br />
moist air laterally from the irrigated cropland; this<br />
causes subsidence <strong>of</strong> air over the cropland, just as<br />
with land–sea breezes. Rising moist air increases precipitation<br />
by 10% over heathland, whereas subsiding<br />
dry air reduces precipitation by 30% over the cropland.<br />
RH, relative humidity.<br />
properties that account for regional zonation<br />
<strong>of</strong> vegetation and land–atmosphere exchange<br />
(Walker and Everett 1991, Walker et al. 1998).<br />
At the global scale, Saharan dust is transported<br />
across the Atlantic Ocean and deposited on the<br />
Amazon by tropical easterlies. Although the<br />
annual input <strong>of</strong> dust is small, it contributes substantially<br />
to soil development over the long<br />
term (Graustein and Armstrong 1983). Similarly,<br />
dust from the Gobi desert is deposited in<br />
the Hawaiian Islands at the rate <strong>of</strong> 0.1gm -2 per<br />
century. In old soils (those more than 2 million<br />
years old), dust input can be the largest source<br />
<strong>of</strong> base cations (Chadwick et al. 1999).<br />
Land–atmosphere exchange <strong>of</strong> water and<br />
energy in one location influences downwind<br />
climate. Oceans and large lakes moderate the<br />
climate <strong>of</strong> adjacent land areas by reducing temperature<br />
extremes and increasing precipitation<br />
(see Chapter 4). Human alteration <strong>of</strong> the land<br />
surface is now occurring so extensively that it<br />
also has significant effects on downwind <strong>ecosystem</strong>s.<br />
Conversion <strong>of</strong> Australian heathlands to<br />
agriculture has, for example, increased precipitation<br />
over heathlands and reduced it by 30%<br />
over agricultural areas (Fig. 14.10) (see Chapter