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Could herbivores remove a high fraction of the net primary production in an ecosystem without depressing the standing crop of plants? How might this happen?

Short Answer

Expert verified
Yes, herbivores can remove large amounts of NPP without lowering plant biomass if plants regrow rapidly and nutrient cycling is efficient.

Step by step solution

01

Understanding Net Primary Production

Net primary production (NPP) is the rate at which plants in an ecosystem produce net useful chemical energy; it is the amount of carbon uptake after subtracting Plant Respiration (RES) from Gross Primary Production (GPP). It represents the energy available to the rest of the ecosystem.
02

Role of Herbivores in Ecosystems

Herbivores feed on plants and can potentially consume large portions of the plant biomass. However, this does not necessarily lead to a long-term decrease in plant biomass if other conditions such as plant growth rates or herbivore efficiency allow for balance.
03

Balancing Herbivory and Plant Growth

In some ecosystems, plants have adapted to grow back quickly after being eaten. Additionally, herbivores often increase nutrient cycling by decomposing plant material rapidly, which can enhance plant regrowth and NPP, achieving a balance between consumption and production.
04

Adaptations Enhancing Plant Resilience

Plants may develop structural or chemical defenses that limit the amount of biomass consumed by herbivores or make it less appealing, allowing them to maintain standing crops despite high rates of consumption.
05

Ecological and Environmental Factors

External factors like environmental conditions, predator presence controlling herbivore populations, or plant species diversity can also influence the impact herbivores have on the standing crop and NPP. These factors can maintain or even enhance plant productivity despite high levels of herbivory.

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Key Concepts

These are the key concepts you need to understand to accurately answer the question.

Herbivory in ecosystems
Herbivores play a crucial role in ecosystems by consuming plant materials as their primary source of nutrition. The relationship between herbivores and plants is complex and can vary based on numerous factors, including plant species, environmental conditions, and the presence of predators.
The digestion of plant material by herbivores aids in nutrient recycling, as herbivores break down the plant cells, releasing essential nutrients back into the soil through their waste. This recycling process is a vital component for sustaining the ecosystem's health and productivity. Moreover, herbivores can influence plant community dynamics by preferentially feeding on certain plant species, which can affect plant species composition and diversity.
In some instances, even if herbivores consume large amounts of plant biomass, the ecosystem remains resilient due to efficient plant growth and ecological adaptation mechanisms. Thus, herbivores are not just consumers but also key facilitators of energy transfer and nutrient cycling within ecosystems.
Plant growth and resilience
Plants have evolved a variety of strategies to recover from being fed upon by herbivores. These strategies enable plants to maintain their standing biomass despite herbivore pressure.
One effective adaptation is rapid shoot or leaf regrowth following damage. This ability allows plants to quickly replenish what herbivores have consumed. Additionally, some plants may increase their photosynthetic rates temporarily to boost their energy production and support regrowth.
Plants can also produce structural defenses, like tough leaves or spines, and chemical defenses, such as toxins, to deter herbivory. These defenses can prevent excessive consumption and ensure enough plant material remains to sustain growth. Together, these adaptations contribute to maintaining net primary production even with herbivore presence.
Nutrient cycling
Nutrient cycling is essential to ecosystem functioning and plant productivity. When herbivores consume plants, they facilitate nutrient cycling by transforming plant biomass into waste products. These waste products decompose rapidly, enriching the soil with nutrients necessary for new plant growth.
This cycling does not just replenish essential minerals in the soil but also helps stimulate microbial activity. Microorganisms break down organic material further, releasing additional nutrients that are readily absorbed by plant roots. This process helps maintain plant health and supports sustainable growth.
As a result, nutrient cycling ensures that ecosystems remain productive and resilient, enabling plants to recover from consumption by herbivores and contributing to balanced energy flows within the system.
Ecological adaptations
Ecological adaptations are essential for plants and ecosystems to thrive under the pressure of herbivores. These adaptations involve changes in behavior, morphology, and physiology to better survive and reproduce in the presence of herbivores.
For instance, many plants develop symbiotic relationships with other species, such as insects or fungi, which help protect against herbivores or enhance nutrient uptake. Additionally, plants may alter their chemical composition to become less palatable or more toxic to deter herbivore consumption effectively.
Environmental conditions, like climate and soil type, also influence plant and herbivore interactions, affecting how plants adapt to herbivory. Facing these pressures, plants can change phenotypically over time, enhancing their resilience and ability to maintain or improve net primary production in the face of ongoing herbivory.

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Most popular questions from this chapter

How would you expect trophic level biomass to change as the primary productivity of the community increases? Use your knowledge about hypotheses of community organization and discuss the assumptions underlying your predictions. Compare your expectations with those of Power (1992).

In discussing the reality of trophic levels, Murdoch \((1966 a, p .219)\) states: Unlike populations, trophic levels are ill-defined and have no distinguishable lateral limits; in addition, tens of thousands of insect species, for example, live in more than one trophic level either simultaneously or at different stages of their life histories. Thus trophic levels exist only as abstractions, and unlike populations they have no empirically measurable properties or parameters. Discuss.

Does any increase in primary production lead to an increase in herbivore grazing pressure, thus maintaining a low standing crop of plants? Discuss what ecological processes might prevent this from happening. Van de Koppel et al. (1996) discuss this question and provide data from a salt marsh grazed by hares, rabbits, and geese.

Population density (no. of individuals per \(\mathrm{m}^{2}\) ) of all organisms in all ecosystems falls with increasing body size, so that larger animals are less common. But for species of equal body size, aquatic organisms are \(10-20\) times more abundant in lakes than terrestrial organisms on land. Suggest two reasons why this might be. Cyr et al. (1997) discuss this issue.

How would it be possible to have an inverted Eltonian pyramid of numbers in which, for example, the standing crop of large animals is larger than the standing crop of smaller animals? In what types of communities could this occur? Do Eltonian pyramids apply to both animals and plants? Del Giorgio et al. (1999) discuss these issues.

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