Testimony of David L. Sunding
Professor, UC Berkeley
regarding
submitted to the Subcommittee on
Fisheries, Wildlife and Water
Committee on Environment and Public Works
U.S. Senate
April 10, 2003
Mr.
Chairman and members of the subcommittee, I appreciate the opportunity to speak
with you today about the economic impacts of critical habitat designation. I am
a professor of natural resource economics at UC Berkeley, and my areas of
interest include wetlands and endangered species policy, housing and land
markets, and water resources.
For
the past two years, I have worked with colleagues and students at Berkeley to
understand the effects of environmental permitting on the process of urban
growth and development. As part of this larger research program, I have had the
opportunity to consider the effects of critical habitat designation, in
particular its impact on the timing and intensity of development; the
availability of housing, roads and other needed infrastructure; and the costs
of designation to consumers, developers, landowners and other groups.
Critical
habitat designation has numerous economic impacts, including the following:
Costs of completing a Section 7
consultation. Section 7
of the Endangered Species Act requires federal agencies to consult with the
U.S. Fish & Wildlife Service to insure that any activity funded, carried
out or authorized will not likely jeopardize the continued existence of the
species. This requirement increases the cost to complete the project, and also
imposes additional costs on federal agencies involved with the consultation.
Sources of cost to the applicant include hiring outside consultants and
attorneys to assist with the consultation process, and also the developer’s own
staff resources.
Another
direct cost of Section 7 consultation is that the Service may require
additional mitigation above that required by the action agency. In the case of
California vernal pools, for example, the USFWS required that three acres of
vernal pools be created for every one filled over and above the baseline. Adding the costs of the Section 7
consultation to the costs of mitigation, the direct, out-of-pocket cost of
Section 7 consultation can be substantial, running to several thousand dollars
per house in the case of some single-family housing projects.
Costs of project modification. The Section 7 consultation process may
also force project developers to redesign their project to avoid modification
of certain areas deemed to be critical habitat. This project redesign typically
reduces the output of the project. Again using the vernal pool case as an
example, additional Section 7 conservation requirements consist of avoidance of
85.7 percent of vernal pools, a condition that allows only 14.3 percent of the
project site to be developed. Project redesign imposes additional costs on
developers and has other, potentially large, economic impacts that stem from
the attendant reduction in output, particularly in areas like California that
have a well-documented shortage of housing and urban infrastructure.
Increase in
price and reduction in the availability of housing and other development. Because critical habitat designation increases the
cost of development and reduces the level of project output, it has the
potential to alter regional markets for housing, commercial space and other
types of development. In particular, critical habitat designation can increase
market prices for these goods and result in large losses to consumers.
Whether
for homes, schools, or other activities, there are numerous physical and
regulatory constraints on site selection.
Accordingly, if critical habitat designation places some land off-limits
to development, there are a limited number of comparable sites that can be
developed to pick up the slack. While an area may appear to have an ample
supply of developable land, in reality the development process is highly
constrained. In such a setting, critical habitat designation can reduce the
regional stock of housing and other goods, and prices of these goods will
increase to establish new market equilibria.
Delay in completion of projects. Critical habitat designation can also
delay completion of projects. Unlike the supply reduction effects just
described, delay is a pure loss
affecting both producers and consumers. Theoretical results suggest that in
many cases delay can be the largest component of overall economic impact
resulting from environmental regulation.
Delay
affects project developers by pushing out project receipts further into the
future. Delay affects consumers in that they must postpone the enjoyment of the
project output. For example, if the project is to construct a school, then
parents and children must wait to use the new facilities; if the project is to
construct new homes, then homeowners must live temporarily in a less than
optimal location, perhaps having to commute longer distances during this
waiting period.
Economic losses borne primarily by
consumers. The economic
impacts of critical habitat designation are borne mainly by consumers. Cost
increases can be passed on to consumers to some degree, and increases in market
price of project outputs actually benefit producers.
A
stylized example can help to provide some sense of the magnitude of impacts and
their distribution across the affected population. Consider a 1,000-unit
housing project to be built on 200 acres (an average of 5 homes per acre,
including roads, open spaces and other infrastructure). The pre-regulation
price of the homes in the project is $250,000, and the elasticity of demand for
these homes is –1.67. The pre-regulation marginal cost of homes in
the project is assumed to be a constant $200,000.
Suppose
that some of the project is considered to be critical habitat; development is
to be avoided in these areas and any habitat impacts mitigated by some ratio of
the USFWS’ choosing. Suppose that the out-of-pocket cost to the developer of
the Section 7 consultation, including the mitigation exaction, is $2,000 per
home. Suppose also that critical habitat designation reduces the size of the
project to a total of 900 units instead of the planned 1,000. Finally, suppose
that critical habitat concerns delay completion of the project by two years.
Based
on these figures, what are the economic impacts of critical habitat designation
for this hypothetical project? Homes in the project are now more expensive to
construct and there are fewer of them, so their market price will increase.
Under the assumptions above, the price of a home in the project will increase
from $250,000 to $265,000.
Consumers
lose from critical habitat designation in three ways. Some are unable to
purchase homes at all due to the reduction in the size of the project. Some do
purchase homes, but at higher prices. And what consumption does occur is two
years later than it would have been without the critical habitat designation.
The impacts of permitting on developers (and landowners) are more complex.
While producers gain from the increase in home prices, they lose from the
increase in costs and from the delay in completing the project and receiving
their return on investment.
Taking
consumers and producers together, the total economic losses from critical
habitat designation are $19.5 million for this project. This figure counts the
cost of project delay, which amounts to $12.5 million, or over half of total
losses. While permitting reduces the size of the project from 1,000 to 900
completed units (which results mainly in losses to consumers), both consumers and
producers must wait an extra two years for these 900 units to be completed.
Several interesting conclusions emerge from this example:
·
Critical
habitat designation can be quite expensive. Total economic losses amount to
nearly $20 million in the example, which implies costs of $1 million per acre of habitat conserved.
·
Consumers
bear the brunt of losses from critical habitat designation. They are
unambiguously harmed by increases in price and reductions in the number of
homes available for purchase. Developers and landowners fare better because
they can pass on some costs to consumers and because they benefit from price
increases.
·
Traditional
measures of the cost of regulation, namely the out-of-pocket cost of Section 7
consultation, are far off the mark. In this example, they understate true
impacts by an order of magnitude.
Regional and indirect impacts: Is
conservation good for the environment?
Critical habitat designation is effectively an ad hoc tax on development that
changes its intensity, location and timing. As such, critical habitat
designation can literally change the shape of urban areas, and another class of
economic impacts results.
A
natural question to ask is whether, by limiting growth in certain areas,
critical habitat designation pushes development to areas more distant from the
city center, away from jobs, shopping areas, schools and other amenities. If
the effect of critical habitat designation is to force relocation to areas
further out on the urban fringe, there can be some important regional and
indirect consequences of designation as well. For example, if critical habitat
designation forces commuters to locate further from their jobs, then
designation may increase traffic congestion and commute times, and may
contribute to regional problems of sprawl and air pollution.
Impacts beyond the federal nexus. A common claim of the USFWS is that critical habitat designation only causes economic impacts in the presence of a federal nexus, that is if the activity in question is carried out with a federal permit or federal funding. While there is no definitive research on this topic, my work with developers, local government officials and others suggests that critical habitat designation has more far-reaching implications.
One concern is that development is subject to numerous regulatory
processes carried out by federal, state and local authorities. If land is
designated as critical habitat by the USFWS, this designation may affect the
way the project is treated by other agencies through a “signaling” effect. At a conceptual level, this signaling effect
is not surprising. Regulators operate under uncertainty and are generally
risk-averse. A decision by an expert environmental
agency like the USFWS raises concerns about potential environmental impacts of
the project and will lead other permitting agencies to take a more conservative
approach to it. From a practical point
of view, this signaling effect means that the costs of critical habitat
designation go beyond the cost and the outcome of the Section 7 consultation
process.
Another
concern is that designation of critical habitat can impose costs on developers
even if their project is not on critical habitat at all. The USFWS defines
critical habitat in such a way that some time and expense is needed to
determine whether a parcel is actually included or not. For example, critical
habitat is defined in terms of landscape features and some investigation is
required to determine their presence or absence on a particular parcel. Again,
the practical effect is for the costs of critical habitat designation to extend
beyond the Section 7 process.