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The establishment of duck hunting regulations involves such
things as the number of days the season will be open, how many
ducks to allow in the bag limit, how many mallards and other
species to allow to be taken each day and what beginning and ending
dates are suitable. In the past, those decisions have involved
politics, the opinions of professional migratory bird managers and
others, and the social need to "do something" when a
population level is low. All those factors are affected by the
status of waterfowl populations and the understanding of the
relationships among populations, regulations and harvest
Before 1995, decisions were made based on discussions that
sounded something like this: "I think the bag limit should be
lower than last year's because ducks are down." "I
think an increase in season length by seven days is too many."
"Ducks are up so we can liberalize the bag limit but not
season length." "Ducks are up, so let us hunt more days -
we will leave the bag limit alone." "The data shows that
mallard survival rates have not changed over the years, so give our
hunters 60 days to hunt and leave the bag limit at five and
let's go to work on habitat." "Close the duck
season."
In many ways, the system worked. Population levels and the
associated hunting opportunities have been maintained in spite of
greatly varying habitat conditions. Nevertheless, there has been
much uncertainty about the effect of regulations on harvest and, in
turn, on duck populations. To help resolve that uncertainty, a
process called Adaptive Harvest Management (AHM) was proposed in
the early 1990s. This is a specific implementation of a broader
process called Adaptive Resource Management. (learn more)
AHM provides a more objective, better-informed and less
contentious decision-making process; an explicitly defined role for
monitoring programs; and a formal and coherent framework for
addressing controversial harvest management issues. The system
includes explicit statements about the uncertainty of the
information included. For example, the exact size of the mallard
population and the exact harvest rate are not known. ARM also
includes a "learning" objective - the system is
constructed so that the rate of learning is identified and all
information learned is explicitly incorporated into the next round
of decision-making. An environment is achieved in which achievement
of management objectives can be measured.
That computers and models are an important tool in AHM should
surprise no one. AHM is data hungry: Pond counts must be related to
bird counts; harvest data must be related to band and band
reporting data and to bird counts; biological parameters such as
survival and production rates must be related to bird counts and
harvest; harvest characteristics must be related to regulations;
and many years' data from many regions of the continent must be
considered.
While it would be ideal if there was agreement about the nature
of those relationships by all parties, agreement is not necessary
for AHM to succeed. That is where the "learning"
component comes in. Several different relationships can be
described by models that use much of the same data. Currently there
are four AHM models encompassing the broad theories associated with
relationships between mortality caused by hunting and mortality
caused by other factors. Further, two different theories about
mallard reproduction are included.
If at least one of the models accurately represents the
"real" world, all four can be run and let the data and
assumptions produce a prediction about, for example, mallard
population size. The accuracy of the four predictions can be
measured and, eventually, scientists can learn which hypothesis is
correct. In addition, an evaluation of how well the models depict
the real world can occur and needed modifications can be made to
them.
Since 1997 and into 2000, the models have incorporated four
alternatives for hunting seasons labeled according to content: very
restrictive, restrictive, moderate and liberal. Each regulatory
package contains a set of frameworks for each of the four flyways
(for example, the liberal alternative contains a 60 day duck season
for the Mississippi Flyway and 74 days for the Central). Since the
best data is available for mallards and they are one of the most
heavily harvested of all duck species, each regulatory package has
a target harvest rate (the percent of the population harvested) for
mallards associated with it. When the models are run, the results
are weighted by several factors and an "optimal" harvest
alternative is identified. Once the computer has completed its
tasks, it is still up to people (wildlife agency administrators,
biologists and the public) to select a regulatory package for the
current year. However, they now can do this with a great deal more
confidence and considerably less controversy than in the years
before AHM.
Each year, current survey data is included with historical data
and included in new model runs. The predictions of the models are
compared to the results of surveys and adjustments to some model
parameters can be made. Thus, waterfowl managers learn a little
more about the complex relationships of regulations, harvest and
duck populations.
Adaptive Harvest Management for ducks is in its infancy.
Including other duck species will take years, but some interim
models for pintails and canvasbacks have been implemented, allowing
an objective approach to establishing hunting regulations and
avoiding knee-jerk reactions to changes in harvest or survey
results. In 2000, new models were available to consider an eastern
mallard population and its interaction with a much larger
mid-continent population which largely supplies mallards for most
of the United States.
The alternative to AHM is a return to days of setting duck
hunting regulations in a more contentious atmosphere and one driven
less on science than on opinion. It is the view of the CFC that
this is not a good alternative and support for AHM remains high.
(learn more about AHM - link to FWS report).
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