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Principles of terrestrial ecosystem ecology.pdf

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108 5. Carbon Input to Terrestrial Ecosystems<br />

carbon fixation by the canopy as a whole. This<br />

is one <strong>of</strong> many examples in <strong>ecosystem</strong> <strong>ecology</strong><br />

in which selection for optimal performance at<br />

the level <strong>of</strong> individuals gives rise to predictable<br />

patterns at the level <strong>of</strong> <strong>ecosystem</strong>s.<br />

Leaf area is the major factor governing the<br />

light environment experienced by individual<br />

leaves within the canopy. There is a maximum<br />

leaf area that plants in an <strong>ecosystem</strong> can attain,<br />

because light is a directional resource that is<br />

greatest at the top <strong>of</strong> the canopy and decreases<br />

exponentially within the canopy, according to<br />

the following equation:<br />

I = I0e -kL (5.1)<br />

where I is the irradiance (the quantity <strong>of</strong><br />

radiant energy received at a surface per unit<br />

time) at any point in the canopy, Io is the irradiance<br />

at the top <strong>of</strong> the canopy; k is the extinction<br />

coefficient, and L is the projected leaf area<br />

index (LAI; the leaf area per unit <strong>of</strong> ground<br />

area) above the point <strong>of</strong> measurement.<br />

LAI is a key parameter governing <strong>ecosystem</strong><br />

processes because it determines the light attenuation<br />

through a canopy and strongly influences<br />

the capacity <strong>of</strong> vegetation to gain carbon<br />

and transfer water and energy to the atmosphere<br />

(see Chapter 4). LAI has been defined in<br />

two ways: (1) Projected LAI is the leaf area<br />

projected onto a horizontal plane. (2) Total<br />

LAI is the total surface area <strong>of</strong> leaves, including<br />

the upper and lower surface <strong>of</strong> flat leaves<br />

and the cylindrical surface <strong>of</strong> conifer needles.<br />

Total LAI is approximately twice the value <strong>of</strong><br />

projected LAI, except in the case <strong>of</strong> conifer<br />

needles, for which the projected leaf area is<br />

multiplied by p (3.14) to get total leaf area.<br />

Total LAI is particularly useful in describing<br />

the effective leaf area <strong>of</strong> conifer forests, in<br />

which leaves are more cylindrical than flat. A<br />

flat leaf cannot absorb more photons than<br />

move through a horizontal plane, because light<br />

is a directional resource. Conifer needles can,<br />

however, absorb considerably more light per<br />

unit <strong>of</strong> projected leaf area than flat leaves.<br />

Conifer needles are particularly effective in<br />

absorbing diffuse light, which provides a more<br />

uniform illumination <strong>of</strong> the overall canopy.<br />

Diffuse light makes up a larger proportion <strong>of</strong><br />

total irradiance at low sun angles and under<br />

cloudy conditions. This may explain the predominance<br />

<strong>of</strong> conifers in high-latitude forests,<br />

where sun angles are low and in temperate<br />

rain forests, where conditions are usually<br />

cloudy. Unfortunately, there is no consistent<br />

agreement on whether data should be<br />

expressed as projected LAI or total LAI, and<br />

many review papers do not specify clearly<br />

which definition <strong>of</strong> LAI is being used. Micrometeorologists<br />

measuring radiation transfer and<br />

ecologists working with broad-leaved forests<br />

tend to use projected LAI, whereas ecophysiologists<br />

interested in carbon exchange and<br />

ecologists working in conifer forests tend to use<br />

total LAI. Each definition <strong>of</strong> LAI has advantages<br />

for addressing particular questions. The<br />

important thing is to specify which definition is<br />

being used.<br />

Projected LAI varies widely among <strong>ecosystem</strong>s<br />

but typically has values <strong>of</strong> 1 to 8m 2 leaf<br />

m -2 ground for <strong>ecosystem</strong>s with a closed<br />

canopy. The extinction coefficient is a constant<br />

that describes the exponential decrease in irradiance<br />

through a canopy. It is low for vertically<br />

inclined or small leaves (e.g., 0.3 to 0.5 for<br />

grasses), allowing substantial light penetration<br />

into the canopy, but high for near-horizontal<br />

leaves (0.7 to 0.8). Clumping <strong>of</strong> leaves around<br />

stems, as in conifers, and variable leaf angles<br />

result in intermediate values for k. Equation 5.1<br />

indicates that light is distributed unevenly in an<br />

<strong>ecosystem</strong> and that the leaves near the top <strong>of</strong><br />

the canopy capture most <strong>of</strong> the available light.<br />

Irradiance at the ground surface <strong>of</strong> a forest, for<br />

example, is <strong>of</strong>ten only 1 to 2% <strong>of</strong> that at the top<br />

<strong>of</strong> the canopy. At very low irradiance, leaf<br />

respiration completely <strong>of</strong>fsets photosynthetic<br />

carbon gain, resulting in zero net photosynthesis,<br />

the light compensation point <strong>of</strong> the leaf (Fig.<br />

5.8). A mature shaded leaf typically does not<br />

import carbon from the rest <strong>of</strong> the plant, so the<br />

leaf senesces and dies if it falls below the light<br />

compensation point for extended periods <strong>of</strong><br />

time. This puts an upper limit on the leaf area<br />

that an <strong>ecosystem</strong> can support, regardless <strong>of</strong><br />

how favorable the climate and the supply <strong>of</strong> soil<br />

resources may be.<br />

Do differences in light availability explain<br />

the differences among <strong>ecosystem</strong>s in carbon<br />

gain? In midsummer, when plants <strong>of</strong> most

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