Toward construction of an inclusive model for desertification - some new methds and concepts

We've been working with some conceptional framework of the simulation models which describe the processes of "desertification". The objective of our team is to construct the appropriate guideline to construct the simulation model and to propose a new paradigm of ecological models.

Environmental conditions of desertification effective to plants
The term "desertification" should be used with the view point of the effectiveness of its environmental conditions to plants. Because the strict meaning of "desertification" is the decline or elimination of the vegetation caused by drought, the major effective environmental conditions can be easily determined. That is, water shortage, salt accumulation and soil erosion.

How many plant responses should be considered ?
Plant responses to these three environmental conditions must be divided in to two levels; physiological responses and reproductive responses. Physiological responses are examined mainly on the level below the individual plants. Reproductive responses, which has been often called as ecological responses, are studied on the level higher than the individual plants, and mainly on the population-level. Thus, we must consider 3x2=6 components to describe the plant responses to drought and the process of "desertification".

Temporal and spacial nature - heterogeneity
Spatial distributions of the three environmental conditions are characterized by its heavy heterogeneity. It is now strongly proposed that the spatial heterogeneity of the environmental conditions plays a key role to maintain plant species survival. We must include the spatial heterogeneity of the environmental conditions into our model.
Temporal distribution of the environmental conditions are characterized by its deep unpredictability. Suppose that the rainfall pattern at a certain desert. Such an deep unpredictability is quite critical and often lethal to all plant species. Thus, we can't exclude the unpredictability of the environmental conditions from our model.

Importance of individual-based models (IBMs)
Individual-based models (IBMs) are categorized as analytical mathematics model and Monte-Caro-type simulation models. The most prominent difference of IBMs from the previous models is its structure.
Unlikely to the old models, the IBMs are constructed based on the characteristics of individuals. For example, most of the old-styled forest dynamics models consisted of a series of size or age classes. In these models, the informations about positions of each trees and/or those about structure of crown were neglected. IBMs do, however, consist of individual trees with specific positions and canopy structures.
The IBMs have three useful features. The first is their ability to make connections between phenomena at different levels of biological organization. It can elucidate the consequence of individual responses to population and community responses to environmental conditions. The second is that they can examine the effects of high heterogeneity and high stochasticity (or, say, uncertainty) of environments on biological communities. The third is their usage as correction methods for general theories. For example, much of competition theory in ecology is at the population level, and is not tested at the individual level. The IBMs must give some corrections to the theories based on population.

Additional viewpoint - chaos
It is well-known that some complicated systems often show chaotic behavior. The IBMs also sometimes show the chaotic behavior. They often return to regular or random behavior after a certain period of chaos, and they may go to chaos again. This is because some chaotic systems have "window". In this window, some regular or random pattern can be seen. As the desertification is a kind of simplification of vegetation, it must be useful to consider the "window" of the chaotic system.

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