Anti-conservation incentives: the Endangered Species Act is endangering species.
Adler, Jonathan H.
In early 2006, landowners in Boiling Springs Lakes, N.C., began
clear-cutting timber from their property after the U.S. Fish and
Wildlife Service (FWS) announced that development could threaten local
red-cockaded woodpecker populations. The FWS released a map showing
clusters of the woodpecker in the area and announced plans to identify
additional habitat for the endangered bird. That prompted landowners to
grab their chainsaws to clear their property of the trees in which the
woodpeckers make their homes before their land could be designated as
endangered species habitat.
Residents of Boiling Springs Lakes are not anti-environmental or
particularly hostile to endangered birds. Red-cockaded woodpeckers have
thrived there for years. "People are just afraid a bird might fly
in and make a nest and their property is worth nothing," Boiling
Springs Lakes mayor Joan Kinney told local papers. "It is causing a
tremendous amount of clear-cutting." As one local resident told a
reporter, "You had to get in line to get somebody with a chain
saw.... I have not a single pine tree left. Folks around here are
terrified of the prospect of losing their property. That causes people
to get out there and find out what they can do to protect
themselves." In just eight months, the city issued 368 logging
permits but few building permits, leaving many empty lots throughout the
area.
The rampant clear-cutting in Boiling Springs Lakes was a
predictable, if highly regrettable, consequence of the economic
incentives the Endangered Species Act (ESA) creates for private
landowners. Under Section 9 of the act, it is illegal for a private
landowner to engage in activities that could "harm" an
endangered species, including habitat modification, without first
obtaining a federal permit. Knowing violations can lead to fines of up
to $25,000 and even jail time. As a practical matter, the law requires
private landowners to obtain permission from the FWS before modifying
endangered species habitat on their own land. However, it is not illegal
to modify land that might become endangered species habitat some day in
the future, nor are landowners required to take affirmative steps to
maintain endangered species habitat. So, in Boiling Springs Lakes as
elsewhere, landowners seek to avoid the burden of the ESA by eliminating
potential species habitat on their land.
ANECDOTES AND DATA
Economists have been critical of the ESA's perverse incentives
for years. In the most basic terms, the act penalizes and thus
discourages the creation and maintenance of species habitat on private
land. According to University of Arizona economist Robert Innes,
"the possibility of uncompensated takings gives landowners an
incentive to develop their property early on in order to reduce the risk
that it will later be appropriated for public use." Such incentives
have consequences. As Robert J. Smith wrote in Regulation 15 years ago,
"The perverse incentive structure of the act accelerates
destruction of the very habitat the act was designed to protect."
Anecdotal accounts of landowners who have sought to avoid having
"endangered species problems" on their land are rampant. In
Texas, property owners raze juniper tree stands favored by
golden-cheeked warblers, while in California's Central Valley
landowners disc brush and low-lying habitat favored by small endangered
mammals such as kangaroo rats. There are even stories of landowners who
"shoot, shovel, and shut up" when they encounter endangered
species on or near their land.
Some environmental activists dismiss anecdotal accounts of the
ESA's perverse incentives. "Anecdote is not the singular of
data," they explain, stressing that the occasional horror story does not demonstrate that there is something fundamentally wrong with
the act. But others have begun to recognize that the ESA's perverse
incentives can create real problems for species conservation. Writing in
Conservation Biology, a group of wildlife biologists observed that
"the regulatory approach to conserving endangered species and
diminishing habitats has created anti-conservation sentiment among many
private landowners who view endangered species as economic
liabilities." As they explain,
Landowners fear a decline in
the value of their properties
because the esa restricts
future land-use options where
threatened or endangered
species are found [near] by
[and] makes no provisions for
compensation. Consequently,
endangered species are
perceived by many landowners
as a financial liability, resulting
in anticonservation incentives
because maintaining
high-quality habitats that
harbor or attract endangered
species would represent a
gamble against loss of future
opportunities.
[ILLUSTRATION OMITTED]
The policy question today is not whether the ESA creates incentives
for private landowners to work against the conservation of endangered
species, but whether those incentives are so pervasive that the act is
actually doing more harm than good.
EMPIRICAL EVIDENCE
Where there was once little more than economic theory and anecdotal
accounts upon which to criticize the performance of the ESA, today there
is a growing body of empirical evidence that the act's regulatory
provisions undermine species conservation on private land. Four recent
studies show that the incentives created by the ESA cause systematic
changes in private landowner behavior to the detriment of habitat
conservation efforts. Taken together, the studies provide powerful
evidence that the ESA may be endangering endangered species on private
land.
In 2003, Dean Lueck and Jeffrey Michael published a paper in the
Journal of Law and Economics examining the effect of endangered
red-cockaded woodpecker populations on timber management practices m
North Carolina. Specifically, the study looked at whether private
landowners engage in preemptive habitat destruction when the presence of
the woodpeckers places landowners at risk of federal regulation and a
loss of their timber investment.
Consistent with economic theory, Lueck and Michael found that
"increases in the probability of ESA land-use restrictions, as
measured by a landowner's proximity to existing [woodpecker]
colonies, increase the probability of forest harvest and decrease the
age at which timber is harvested." Providing habitat for a single
red-cockaded woodpecker colony can cost up to $200,000 in foregone
timber harvests. To avoid the loss, landowners at greatest risk of
ESA-imposed restrictions were most likely to harvest their forestlands
prematurely and reduce the length of their timber harvesting rotations.
Cutting timber stands prematurely deprives red-cockaded woodpeckers of
habitat because the birds only inhabit older trees. According to the
Lueck-Michael study, the ultimate consequences were potentially
significant, amounting to several thousand acres of lost woodpecker
habitat, enough to provide habitat for between 25 and 76 red-cockaded
woodpecker colonies. That is a significant habitat loss for a species
dependent upon private land for its survival.
A second study on the effect of red-cockaded woodpecker populations
on timber practices by Daowei Zhang in Economic Inquiry reinforced the
Lueck and Michael findings. Zhang found that "regulatory
uncertainty and lack of positive economic incentives alter landowner
timber harvesting behavior and hinder endangered species conservation on
private lands." Absent such uncertainty, "landowners choose
among harvesting methods to maximize stumpage revenue ... subject to
constraints such as forest stand characteristics ..., aesthetics,
management objective, and tax liability." The threat of regulatory
prohibitions on timber activity under the ESA, however, alters
landowners' calculations. Zhang found that "a landowner is 25%
more likely to cut forests when he or she knows or perceives that a
red-cockaded woodpecker cluster is within a mile of the land than
otherwise." The threat of ESA regulation also increases the
likelihood that a landowner would engage in clear-cutting when
harvesting the timber, as opposed to a selective harvesting technique
that may have less ecological impact. On that basis, Zhang concluded,
"at least for the [woodpecker], the ESA has a strong negative
effect on habitat," and the effect appears to be
"substantial."
Zhang's results largely confirm the Lueck-Michael findings. As
Zhang reported,
Despite the use of different data, the basic conclusions reached in
these two studies are similar: the ESA regulations actually lead
landowners [to] cut their timber sooner, to the detriment of the
[red-cockaded woodpecker], than they otherwise would do. As a
consequence, [woodpecker] habitats have been reduced on private
lands because of the ESA. In this case the ESA imposes costs but
does not generate conservation benefits.
The perverse incentives of the ESA do not simply affect the
woodpeckers and other species dependent upon private timberland in the
southeastern United States. A study by environmental researchers Amara
Brook, Michaela Zint, and Raymond de Young published in Conservation
Biology looked at landowner responses to the listing of the endangered
Preble's Meadow jumping mouse, a small, nocturnal rodent native to
parts of Wyoming and Colorado. The study conducted surveys of private
landowners within the animal's range and found that a significant
number of landowners took actions to make their lands less hospitable to
the mouse after it was listed as an endangered species. While some
landowners sought to improve the quality of the habitat on their land,
the survey responses suggested that "the efforts of landowners who
acted to help the Preble's were cancelled by those who sought to
harm it." On that basis, the study concluded, "The current
regulatory approach to the conservation of rare species is insufficient
to protect the Preble's mouse." Indeed, the authors were
forced to conclude that "as more landowners become aware that their
land contains Preble's habitat, it is likely that the impact on the
species may be negative."
The Brook findings illustrate the factors that motivate landowner
behavior with regard to endangered species. Some landowners indicated a
willingness to help the Preble's Meadow jumping mouse upon hearing
it was endangered, presumably because they wished to help an endangered
species. Their positive reaction was not dependent upon the regulatory
strictures of the ESA but on their belief in the importance of species
conservation or other values. Those landowners who expressed intent to
destroy potential habitat on their land, on the other hand, are unlikely
to have been motivated by a visceral hostility to endangered species or
conservation more broadly. It is more likely that those who took
negative actions did so because of the threat of regulation and its
potential economic consequences. Without ESA regulation, the existence
of the jumping mouse would have posed no economic threat to private
landowners and the likely effect of the mouse's listing would have
been a a net increase in conservation efforts on private lands. Instead,
the positive efforts of some landowners were "cancelled" by
those who took negative actions in response to the act.
The Conservation Biology study also found evidence that the ESA
discourages private landowners from cooperating with environmental
researchers. Specifically, it found that landowners would refuse to give
biologists permission to conduct research on their land to assess mouse
populations out of fear that land-use restrictions would follow the
discovery of a mouse on their land. "Many landowners appeared to
defend themselves against having their land-management options
restricted by refusing to allow surveys for the Preble's," the
Brook study reported. That is a grave concern because accurate data on
species populations and their habitat are essential to successful
conservation efforts. Not only is the ESA discouraging landowners from
maintaining habitat, but the act could be obstructing the accumulation
of data about what species are in need of protection in the first place.
A fourth study of uncompensated ESA regulation by economists John
List, Michael Margolis, and Daniel Osgood sought to measure "the
extent to which landowners act to preempt regulation during the urban
growth process" by accelerating the rate at which land is
developed. The study focused on landowner responses to the threat of
regulation of habitat for the Cactus Ferruginous pygmy owl near Tucson,
Ariz., and found evidence that the threat of ESA regulation accelerates
the rate at which privately owned species habitat is developed.
Specifically, the study found that land designated as critical owl
habitat was, on average, developed one year earlier than equivalent
parcels that were not designated as habitat. This acceleration of
development was facilitated in part because the pygmy owl was listed and
proposed critical habitat was published months before regulatory
responses were imposed, "allowing landowners ample time to
respond." Those findings are reinforced by additional data showing
that the value of undeveloped land designated as critical habitat fell
relative to other lands in the study area. Although as a strict legal
matter critical habitat designation is not necessary for land to be
burdened by the ESA's regulatory strictures, it provides a signal
to landowners about the likelihood of future regulatory restraints.
While the List study focused on the timing of development, it
should be noted that government actions that encourage more rapid
development can be expected to result in more net development. For
ecological purposes, the decision to develop land can be irreversible.
Once habitat is lost, it can be difficult to replace. At the same time,
land that is not developed today can still be conserved or protected
before it is developed tomorrow. Thus, preventing--or, at least,
avoiding creating incentives for--premature development serves the
ultimate goal of ecological conservation.
CONCLUSION
These studies, taken together, provide powerful evidence that the
ESA is discouraging species conservation on private land. Worse, they
suggest that the net effect of the ESA on private land could be
negative. Given that habitat loss and fragmentation represent the
greatest threat to endangered species, this should be of concern to
wildlife conservationists. Indeed, the incentives created by the ESA
should be of even greater concern because private land is indispensable
to environmental conservation.
Most land--approximately two-thirds of the continental United
States--is privately owned. The relative importance of such lands for
the maintenance of species habitat and critical ecological functions is
perhaps even greater. Over three-fourths of those species currently
listed as threatened or endangered under the ESA rely upon private land
for some or all of their habitat, according to the U.S. Government
Accountability Office.
Without active conservation on private lands, meaningful ecological
conservation cannot be achieved--and the available evidence suggests
that it is failing. Only a handful of species listed as endangered or
threatened in the past three decades have "recovered,"
according to the FWS, and it is debatable whether there has been a
single "success" story as a result of the regulation of
habitat modification on private land. Instead, as the recent studies
indicate, there is evidence that ESA regulation may be causing
conservation failures.
Years ago, Aldo Leopold wrote of the need for a new land ethic
among landowners to safeguard and steward the land. Given the dependence
of endangered species on private land, such a land ethic is essential if
many species are going to continue to survive in the wild. Yet today we
are learning that the nation's primary wildlife conservation law
may be doing more harm than good, discouraging the very land ethic
necessary for endangered species' survival. The purpose of the ESA
is to conserve endangered and threatened species. Instead it appears
that the act may be endangering them.
Readings
* "Endangered Species and Timber Harvesting: The Case of
Red-Cockaded Woodpeckers," by Daowei Zhang. Economic Inquiry, Vol.
32 (2004).
* "Evaluating Costs of Conservation," by Martin B. Main,
Fritz M. Roka, and Reed F. Noss. Conservation Biology, Vol. 13 (1999).
* "Is the Endangered Species Act Endangering Species?" by
John A. List, Michael Margolis, and Daniel E. Osgood. NBER Working Paper
No. 12777, December 2006.
* "Landowners' Responses to an Endangered Species Act
Listing and Implications for Encouraging Conservation," by Amara
Brook, Michaela Zint, and Raymond de Young. Conservation Biology, Vol.
17 (2003).
* "Money or Nothing: The Adverse Environmental Consequences of
Uncompensated Regulatory Takings," by Jonathan H. Adler. Boston
College Law Review, Vol. 49 (2008).
* "Preemptive Habitat Destruction under the Endangered Species
Act," by Dean Lueck and Jeffrey Michael. Journal of Law and
Economics, Vol. 46 (2003).
* "Takings, Compensation, and Equal Treatment for Owners of
Developed and Undeveloped Property," by Robert Innes. Journal of
Law and Economics, Vol. 40 (1997).
* "The Endangered Species Act: Saving Species or Stopping
Growth?" by Robert J. Smith. Regulation, Vol. 15, No. 1 (1992).
Jonathan H. Adler is professor of law at the Case Western Reserve
University School of Law and director of the school's Center for
Business Law and Regulation.