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Principles of terrestrial ecosystem ecology.pdf

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254 11. Trophic Dynamics<br />

promote rapid recycling <strong>of</strong> nutrients and therefore<br />

are a key factor supporting the grasslands’<br />

high production (Ruess et al. 1989) (Fig. 11.6).<br />

Consumption efficiencies <strong>of</strong> carnivores are<br />

<strong>of</strong>ten higher than those <strong>of</strong> herbivores, ranging<br />

from 5 to 100%. Vertebrate predators that feed<br />

on vertebrate prey, for example, <strong>of</strong>ten have a<br />

consumption efficiency greater than 50%, indicating<br />

that more <strong>of</strong> their prey is eaten than<br />

enters the soil pool as detritus. Invertebrate<br />

carnivores <strong>of</strong>ten have a lower consumption efficiency<br />

(5 to 25%) than vertebrate carnivores.<br />

Consumption efficiency <strong>of</strong> a trophic level at<br />

the <strong>ecosystem</strong> scale must integrate vertebrate<br />

and invertebrate consumption, including animals<br />

that feed belowground, but these efficiencies<br />

are not well documented at the <strong>ecosystem</strong><br />

scale. More frequently, consumption efficiency<br />

is documented for a single large herbivore for<br />

an <strong>ecosystem</strong> in which it is abundant.<br />

The consumption efficiency <strong>of</strong> a trophic<br />

level depends on the biomass <strong>of</strong> consumers at<br />

that trophic level and factors governing their<br />

food intake. Over the long term, the quantity<br />

and quality <strong>of</strong> available food constitute the<br />

bottom–up controls over the population<br />

dynamics and biomass <strong>of</strong> consumers. In addition,<br />

predators exert top–down controls over<br />

consumer biomass. Bottom–up and top–down<br />

controls frequently interact. Insects feeding on<br />

low-quality foliage, for example, must eat more<br />

food over a longer time to meet their energetic<br />

and nutrient requirements for development.<br />

The longer development time required on<br />

low-quality food increases their vulnerability<br />

to predators and parasites. Rising atmospheric<br />

CO2 concentration, which reduces leaf quality,<br />

for example, <strong>of</strong>ten increases the quantity <strong>of</strong> leaf<br />

material eaten by a caterpiller, because it must<br />

eat more food to meet its energetic requirements<br />

for development (Lindroth 1996). The<br />

resulting increase in development time, however,<br />

probably alters their interactions with<br />

higher trophic levels. Bottom–up controls<br />

related to NPP and food quality <strong>of</strong>ten explain<br />

differences among <strong>ecosystem</strong>s in average consumer<br />

biomass and consumption, with greater<br />

consumer biomass in more productive <strong>ecosystem</strong>s<br />

(Figs. 11.3 and 11.4). Predation, however,<br />

explains much <strong>of</strong> the interannual variation in<br />

consumer biomass and the quantity <strong>of</strong> food<br />

consumed.<br />

People have substantially altered the trophic<br />

dynamics <strong>of</strong> <strong>ecosystem</strong>s through their effects<br />

on consumer biomass. Stocking <strong>of</strong> lakes with<br />

salmonids, for example, increases predation on<br />

smaller fish, such as exotic alewife. Overfishing<br />

can have a variety <strong>of</strong> trophic effects, depending<br />

on the trophic level <strong>of</strong> the target fish. Overfishing<br />

<strong>of</strong> herbivorous fish in coral reefs, for<br />

example, allows macroalgae to escape grazing<br />

pressure and overgrow the corals, killing them<br />

in places. On land, stocking <strong>of</strong> cattle at densities<br />

higher than can be supported by primary<br />

production causes overgrazing and a decrease<br />

in plant biomass; this has led to the loss <strong>of</strong><br />

productive capacity in many arid lands<br />

(Schlesinger et al. 1990). The consequences <strong>of</strong><br />

human impacts on trophic systems are highly<br />

variable, but they <strong>of</strong>ten have pr<strong>of</strong>ound effects<br />

on trophic levels up and down the food chain<br />

as well as on the target species (Pauly and<br />

Christensen 1995).<br />

The bottom–up controls over consumption<br />

efficiency can be described in terms <strong>of</strong> the<br />

factors regulating food intake. Consumption by<br />

individual animals depends on the time available<br />

for eating, the time spent looking for food,<br />

the proportion <strong>of</strong> food that is eaten, and the<br />

rate at which food is consumed and digested.<br />

Each <strong>of</strong> these four determinants <strong>of</strong> consumption<br />

has important ecological, physiological,<br />

morphological, and behavioral controls that<br />

differ among animal species.<br />

Animals do many things other than eating,<br />

including predator avoidance, digestion, reproduction,<br />

and sleeping. In addition, unfavorable<br />

conditions <strong>of</strong>ten restrict the time available for<br />

foraging, especially for poikilothermic animals<br />

such as insects, amphibians, and reptiles, whose<br />

body temperature depends on the environment.<br />

Because <strong>of</strong> these constraints, deer concentrate<br />

their feeding at dawn and dusk; desert<br />

rodents feed primarily at night; bears hibernate<br />

most <strong>of</strong> the winter; and mosquitoes feed most<br />

actively under conditions <strong>of</strong> low wind, moderate<br />

temperatures, and high humidity. Activity<br />

budgets describe the proportion <strong>of</strong> the time<br />

that an animal spends in various activities.<br />

Activity budgets differ among species, seasons,

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