IV.1
What Modeling Is and How It Works
Jerome A. Onsager
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A range manager and a modeler have at least four traits in common.
Both respect intuition and experience, both are subject to bias,
both are exposed to risk, and both do the best they can with the
information that is available. Those range managers who believe
that two or more heads can solve a problem better than one are encouraged
to read on about modeling. In a recent book about modeling insect
populations, Goodenough and McKinion (1992) describe a model as
a representation of a real system, and then define a system as a
collection of a number of elements or components which are interconnected
to form a whole.
How does modeling work? First, modeling uses mathematical symbols
and processes to express relationships that, as scientists and land
managers, we think we understand or that seem reasonable. The knowledge
or logic is greatly condensed into extremely efficient statements
called formulae. This usually is possible only after a lot of clear
thinking, problem definition, and trial-and-error evaluations have
taken place. Next, the formulae are imbedded in a computer program.
Doing this requires a rigid format for reasoning that requires each
user to consider every important element. Finally, the user provides
as many details as possible about as many elements or components
as necessary, after which the model calculates a likely representation
of response by the system.
The least complex systems contain few elements and are open to
few outside influences. A simple example is a hydraulic jack. If
one assumes no leaks and essentially 100-percent efficiency, each
stroke of the handle yields a result that can be predicted exactly.
Rangeland obviously represents an opposite extreme of complexity,
with its multitude of physical forces plus plants and animals of
all sizes, each affecting each other in ways that often are unknown.
As land managers and scientists, we do not pretend that we can precisely
model the entire system, but we are confident that we can model
some elements to a useful degree.
The chapters in this section all discuss interrelationships among
elements or components of rangeland ecosystems that are important
to grasshopper management. A small proportion of that prose already
has been translated into mathematical language and is being used
in the grasshopper model portion of Hopper (the decision support
tool that is described in VI.2).
Examples include the time and rate of grasshopper development as
a function of temperature, forage consumption as a function of grasshopper
size and density, and expected responses of grasshopper populations
to management tactics.
For a variety of reasons, the overwhelming majority of the following
chapters is not yet available in management-oriented models. In
some cases, like soil temperature- egg development relationships,
the information was acquired only recently. In other cases-like
relationships between weather, host plant quality, grasshopper food
consumption, and grasshopper population dynamics- causes and effects
have not yet been precisely quantified. In still other cases, like
predicting outbreaks, scientists and land managers cannot yet calculate
which one of several likely events will eventually occur. The information
nevertheless is being presented in narrative form, intended both
to establish the current state of knowledge about grasshopper population
dynamics and to expedite future modeling efforts.
For additional insights about what modeling is and how it works,
you are encouraged to study appendix A of the Hopper
Users's Guide (VI.2). Also, chapters in section VII discuss
models that probably will be developed in the near future.
Reference
Cited
Goodenough, J. L.; McKinion, J. M. 1992. Basics
of insect modeling. Monogr. 10. St. Joseph, MI: American Society
of Agricultural Engineers. 221 p.
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