06.12.2012 Views

Principles of terrestrial ecosystem ecology.pdf

Principles of terrestrial ecosystem ecology.pdf

Principles of terrestrial ecosystem ecology.pdf

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

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

LAI in dense canopies, because the leaves in<br />

the middle and bottom <strong>of</strong> the canopy contribute<br />

relatively little to GPP. The availability<br />

<strong>of</strong> soil resources, especially water and nutrient<br />

supply, is a critical determinant <strong>of</strong> LAI for<br />

two reasons: Plants in high-resource environments<br />

produce a large amount <strong>of</strong> leaf biomass,<br />

and leaves produced in these environments<br />

have a high SLA—that is, a large leaf area per<br />

unit <strong>of</strong> leaf biomass. As discussed earlier, a high<br />

SLA maximizes light capture and therefore<br />

carbon gain per unit <strong>of</strong> leaf biomass (Fig. 5.12)<br />

(Lambers and Poorter 1992, Reich et al. 1997).<br />

In low-resource environments, plants produce<br />

fewer leaves, and these leaves have a lower<br />

SLA. Ecosystems in these environments have a<br />

low LAI and therefore a low GPP.<br />

Disturbances, herbivory, and pathogens<br />

reduce leaf area below levels that resources can<br />

support. Soil resources and light extinction<br />

through the canopy determine the upper limit<br />

to the leaf area that an <strong>ecosystem</strong> can support.<br />

However, many factors regularly reduce leaf<br />

area below this potential LAI. Drought and<br />

freezing are climatic factors that cause plants to<br />

shed leaves. Other causes <strong>of</strong> leaf loss include<br />

physical disturbances (e.g., fire and wind) and<br />

biotic agents (e.g., herbivores and pathogens).<br />

After major disturbances the remaining plants<br />

may be too small, have too few meristems, or<br />

lack the productive potential to produce the<br />

leaf area that could potentially be supported by<br />

the climate and soil resources <strong>of</strong> a site. For this<br />

reason, LAI tends to increase with time after<br />

disturbance to an asymptote and then (at least<br />

in forests) <strong>of</strong>ten declines in late succession (see<br />

Chapter 13).<br />

Human activities increasingly affect the leaf<br />

area <strong>of</strong> <strong>ecosystem</strong>s in ways that cannot be<br />

predicted from climate. Overgrazing by cattle,<br />

sheep, and goats, for example, directly removes<br />

leaf area and causes shifts to vegetation types<br />

that are less productive and have less leaf area<br />

than would otherwise occur in that climate<br />

zone. Acid rain and other pollutants also cause<br />

leaf loss. Nitrogen deposition can stimulate leaf<br />

production above levels that would be predicted<br />

from climate and soil type. Because <strong>of</strong><br />

human activities, LAI cannot be estimated<br />

simply from correlations with climate. Fortu-<br />

nately, satellites provide the opportunity to<br />

estimate LAI directly. This information is an<br />

important input to global models that calculate<br />

regional patterns <strong>of</strong> carbon input to <strong>terrestrial</strong><br />

<strong>ecosystem</strong>s.<br />

Length <strong>of</strong> the Photosynthetic Season<br />

The length <strong>of</strong> the photosynthetic season<br />

accounts for much <strong>of</strong> the <strong>ecosystem</strong> differences<br />

in GPP. Most <strong>ecosystem</strong>s experience times that<br />

are too cold or too dry for significant photosynthesis<br />

to occur. During winter in cold climates<br />

and times with negligible soil water in<br />

dry climates, plants either die (annuals), lose<br />

their leaves (deciduous plants), or become<br />

physiologically dormant (some evergreen<br />

plants). During these times, there is negligible<br />

carbon uptake by the <strong>ecosystem</strong>, regardless <strong>of</strong><br />

light availability and CO2 concentration. In a<br />

sense, the nonphotosynthetic season is simply a<br />

case <strong>of</strong> extreme environmental stress. Conditions<br />

are so severe that plants gain negligible<br />

carbon. At high latitudes and altitudes and in<br />

dry <strong>ecosystem</strong>s, this is probably the major constraint<br />

on carbon inputs to <strong>ecosystem</strong>s (Fig. 5.1;<br />

see Chapter 6) (Körner 1999). For annuals and<br />

deciduous plants, the lack <strong>of</strong> leaf area is sufficient<br />

to explain the absence <strong>of</strong> photosynthetic<br />

carbon gain in the nongrowing season. Lack<br />

<strong>of</strong> water or extremely low temperatures can,<br />

however, prevent even evergreen plants<br />

from gaining carbon. Some evergreen species<br />

partially disassemble their photosynthetic<br />

machinery during the nongrowing season.<br />

These plants require some time following the<br />

return <strong>of</strong> favorable environmental conditions<br />

to reassemble their photosynthetic machinery<br />

(Bergh and Linder 1999), so not all earlyseason<br />

irradiance is used efficiently to gain<br />

carbon. In tropical <strong>ecosystem</strong>s, however, where<br />

conditions are more continuously favorable<br />

for photosynthesis, leaves maintain their<br />

photosynthetic machinery from the time<br />

they are fully expanded until they are shed.<br />

Models that simulate GPP <strong>of</strong>ten define the<br />

length <strong>of</strong> the photosynthetic season in terms <strong>of</strong><br />

thresholds <strong>of</strong> minimum temperature or moisture<br />

below which plants do not produce leaves<br />

or do not photosynthesize.

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!