Administration Recommends Limiting Tax Breaks To Promote Wetlands.
Administration Recommends Limiting Tax Breaks To Promote Wetlands.
- AuthorsBabbitt, Bruce
- Institutional AuthorsU.S. Department of the Interior
- Cross-ReferenceTax-related excerpts of the Interior Department's report will be
- Code Sections
- Subject Area/Tax Topics
- Index Termsoil and gas taxationAMTagriculture, conservationtimber, reforestation amortizationtimber, reforestation creditgain or loss, timbercapital gains, tax preference
- Jurisdictions
- LanguageEnglish
- Tax Analysts Document NumberDoc 94-6509 (348 pages)
- Tax Analysts Electronic Citation94 TNT 136-38
====== SUMMARY ======
The Clinton administration seeks to promote wetlands conservation by reducing or withdrawing federal financial incentives to developing these areas, according to a recent report issued by the Interior Department. "The Impact of Federal Programs on Wetlands," presented to Congress in March, is the second of two congressionally mandated reports focusing on different wetland areas across the country. The report argues that an approach that focuses on financial incentives such as taxation and subsidies is preferable to vigorous regulation or increased acquisition because it promotes conservation with "a minimum of federal involvement and economic disruption."
Interior states that current tax policies may have the unintended effect of increasing the incentive to drain and convert wetlands. "By lowering the cost of development to the landowner, these tax policies may reduce costs and create incentives to develop more wetlands than would have been developed in the absence of these policies," Interior concludes. The report discusses the impact of the Tax Reform Act of 1986 on wetlands, including changes in the agricultural section of the code regarding the treatment of conversion and development costs, elimination of the preferential tax rate for capital gains, and the alternative minimum tax rules. The report also addresses federal income tax provisions related to forestry, the oil and gas industry, and peat mining.
(Tax-related excerpts of Interior's report appear in this issue of Tax Notes Today.)
====== FULL TEXT ======
A REPORT TO CONGRESS BY THE SECRETARY OF THE INTERIOR
MARCH 1994
THE IMPACTS OF FEDERAL PROGRAMS ON WETLANDS
VOLUME II: The Everglades, Coastal Louisiana, Galveston Bay, Puerto Rico, California's Central Valley, Western Riparian Areas, Southeastern and Western Alaska, The Delmarva Peninsula, North Carolina, Northeastern New Jersey, Michigan, and Nebraska
EXECUTIVE SUMMARY
FOCUS OF THE REPORT
This is the second of two reports to Congress on the impact of Federal programs on wetlands. /1/ Volume I was submitted to Congress in 1988, and examined how Federal programs have affected wet lands in the bottomland hardwoods of the Lower Mississippi Alluvial Plain and the prairie potholes of the Upper Midwest. Volume II focuses on 17 additional study areas, selected because they reflect the broad array of problems facing wetlands nationwide:
o in the South, Florida's Everglades, coastal Louisiana, the
Galveston Bay of Texas, and the Puerto Rican mangroves and
coastal wetlands.
o in the West, California's Central Valley, western riparian
wetlands, and southeastern and western Alaska.
o in the East, the Delmarva Peninsula (comprising parts of
Delaware, Maryland, and Virginia), North Carolina's pocosins
and other freshwater wetlands, and northeastern New Jersey.
o in the Midwest, Michigan's coastal and northern forested
wetlands, and Nebraska's Rainwater Basin.
A map of the study areas for Volumes I and II appears in Chapter 2. (See Figure II-1.)
Volume II is divided into five parts. The four chapters in Part 1 describe the Federal programs affecting wetlands: agriculture, water development and management; infrastructure, local development, and housing; and resource use, extraction, and development. Parts II through V are organized regionally and examine the 17 study areas.
BACKGROUND
THE FUNCTION OF WETLANDS
Wetlands are a vital element in the biosphere and produce numerous benefits for society. They provide critical nursery habitat for many species of fish and wildlife. By temporarily storing large quantities of water, wetlands play an important role in reducing flooding problems and recharging ground water. They help to maintain water quality by filtering out pollutants and sediments, and serve to control erosion by trapping soil washed from nearby uplands. In addition, wetlands are a source of recreation, timber, and other natural products for commercial use. Federal, State, and private conservation actions have slowed but not stopped their disappearance and functional degradation.
THE NATURE AND EXTENT OF WETLAND LOSSES
One hundred and four million acres (47 percent) of the original 221 million acres of wetlands remain in the contiguous 48 States, accounting for 5.0 percent of the land area. Annual losses in the period mid-1970s to mid-1980s averaged 290,000 acres. There are approximately 170 million acres of wetlands in Alaska, with less than 0.1 percent lost over the last 200 years. Lost acreage alone, however, does not depict the full extent of the problem. Few wetlands are in pristine condition. Comprehensive studies of the extent of the degradation are only now beginning, however. /2/
Since the mid-1980s, indications are that wetland losses are slowing. From 1987 to 1990, programs to restore wetlands under the 1985 Food Security Act have added about 90.0 thousand acres to the Nation's wetlands inventory. Other programs to protect wetlands, like the Swampbuster provision of the Food Security Act, have generated support for conserving wetlands. In addition, public education and extension efforts have helped heighten our Nation's awareness of the values of wetlands.
Approximately three-fourths of the remaining wetlands in the continental United States are privately owned. Only about 0.5 percent of these have protective covenants on them. Furthermore, some wetland conversions are not covered by Section 404 of the Clean Water Act (the principal Federal wetlands regulatory program).
The most important economic sector absorbing wetlands is the agricultural sector. As of 1985, 75 million acres of the nation's cropland had been developed by draining land. Significant portions of this drainage were conducted with Federal funds, loans, and technical assistance. Figure I-1 depicts land in organized drainage enterprises.
Digging channels, depositing spoil, and constructing access roads destroys riparian vegetation and reduces or eliminates beneficial filtering, flood control, and erosion control capacity. Once in place, the channels drain wetlands, increasing the rate of runoff which can cause downstream erosion, flooding, and surges of nutrient-loaded water in sensitive coastal marshes.
From the mid-1970s to the mid-1980s, wetland conversions to agricultural land uses accounted for 54.0 percent of the losses. This is an appreciable change from trends observed during the period mid- 1950s to mid-1970s in which agricultural conversion represented 87.0 percent of all wetland losses. This percentage change reflects decreases in wetland acreage lost to agriculture rather than a significant increase in losses from other activities. Urban land use conversions accounted for about 5.0 percent of the wetlands lost from the mid-1970s to the mid-1980s, while conversions to "other" land uses accounted for 41.0 percent of the losses. A word of caution: the substantial portion of conversions classified as "other" is attributable to wetlands that have been cleared and drained, but not yet put to identifiable uses.
THE ECONOMICS OF CONVERSION
That so much wetland conversion has occurred should not be surprising. The United States started with a great abundance of wetlands. With wetlands in abundance, other uses of the land were seen as more valuable. Land was considered to be more valuable when devoted to the production of market goods rather than left in its natural state, producing environmental services and amenities. Further, the initial conversions did relatively little environmental damage. Thus, even if the ecological functions of wetlands had initially been well understood and appreciated (and they usually were not), it would likely have been deemed to be in society's interest to convert wetlands during the early years of development.
Figure I-1: LAND IN ORGANIZED DRAINAGE ENTERPRISES
[Figure omitted]
As with all non-market commodities, however, it is difficult to determine the economic value of wetlands, and so there is no price signal indicating that the value of wetlands increases along with their scarcity and that they merit conservation. Therefore, the normal tendency of a private market is to encourage the conversion of wetlands to other uses. Wetlands constitute a classical example of market failure: the wetland owner generally cannot capture the benefits of his resource for his own use or sale. The flood protection benefits of wetlands accrue to others downstream. Many of the fish and wildlife that breed in and inhabit the wetlands migrate, and are captured or enjoyed by others. The ground water recharge and sediment trapping benefits cannot be commercially exploited. For the owner of a wetland to benefit economically from his resource, he usually has to alter it, convert it, and develop it.
The rate of conversion and development was not left to the determination of an unfettered, private market, however. Starting with the Swamp Lands Acts in 1849 and 1850, government actions supported the conversion and development of wetlands. The Swamp Lands Acts ceded millions of acres of swamp lands to the States with the proviso that the States sell the lands and use the proceeds for reclamation. Programs for flood control, drainage, irrigation, and hydroelectric power grew throughout the 20th century. The projects effected massive changes in the nation's hydrologic regime, and made it both technically feasible and financially attractive to develop the land.
Thus, in years past, the conversion and degradation of major acreages of wetland were the result of both concerted public policy and hundreds of thousands of decisions by people attempting to enhance their economic status. It is only recently that we have realized that wetlands have sufficient value in themselves to warrant preserving most of those remaining. In the interim, many of our wetland and ecosystems have been heavily depleted and are now highly stressed. Thus, although early conversions may have been viewed as a wise use of resources, most wetlands whose conversion would be most lucrative have long been developed, and those remaining are both less desirable from a commercial perspective and more valuable environmentally.
THE CURRENT FEDERAL ROLE
Today, there are a number of Federal programs designed to protect wetlands, but Federal policy is neither comprehensive nor consistent with respect to wetland use. Indeed, Federal programs affect wetlands in opposing ways. Some Federal programs encourage wetland conversion by reducing the cost, increasing the revenue, and/or reducing the risk of wetland development. Simultaneously, other Federal programs restrict or manage wetland use through a variety of techniques and programs: acquisition and easement; regulation; consultation among Federal agencies to identify and either avoid or mitigate the effects of agency actions, and reduction; or withdrawal of Federal financial incentives to develop wetlands.
This report to Congress focuses primarily on the last of these approaches to wetland conservation. Although more vigorous regulation or increased acquisition would preserve more wetlands, these approaches could be costly. The Administration prefers redesigning Federal programs which produce undesired effects on wetlands to additional land acquisition or regulation. This strategy has several appealing features:
o It discourages economically inefficient and environmentally
unsound development.
o It promotes a stronger, more competitive economy by modifying
Federal programs which distort market signals and hamper
initiative.
o It fosters Federal budgetary savings at a time of large
deficits.
o It conserves environmentally significant wetlands with a
minimum of Federal involvement and economic disruption.
Although restricting Federal financial support for unsound development cannot be relied on as the only conservation tool, it should be among the first approaches to the problem of wetland loss. Many Federal programs that affect wetlands are designed and financed in a way that violates the beneficiary-pay principle of public finance. They distort market signals and provide subsidies that have had negative environmental effects. Optimally these programs should be redesigned in order to present those who benefit from the programs and projects with the full cost of their activities. Volume II takes a broad look at over 35 Federal programs implicated in wetland decline, illustrating the range of effects that Federal activities can have on wetland ecosystems.
FINDINGS AND CONCLUSIONS
The following discussion summarizes the background information, findings, and conclusions for the 17 study areas. For each area, the principal causes of wetland loss and functional degradation are identified, and recommendations for future wetland protection are listed. It should be noted that the recommendations are selective, with the purpose of giving the reader insight into the direction of the recommended approach to the problems identified. For the complete set of recommendations, the reader should refer to the end of each area chapter in Parts II through V.
FLORIDA EVERGLADES
1. DESCRIPTION AND IMPORTANCE
o The Everglades hosts a highly diverse spectrum of aquatic
birds, mammals, reptiles, and amphibians.
o The Everglades protects the Biscayne Aquifer, the primary
source of drinking water for the Miami area, by recharging the
ground water, filtering out pollutants, and preventing
saltwater intrusion.
2. EXTENT AND SOURCE OF LOSSES
o The Everglades originally stretched about 100 miles from the
southern end of Lake Okeechobee down to the tidal estuaries of
the Gulf of Mexico and Florida Bay. At the turn of the
century, the Everglades encompassed over 2.3 million acres of
wetlands. By the mid-1970s, about 1.1 million acres (48
percent) of the original acreage remained. Much of the
remaining wetlands is functionally degraded.
o An altered water regime, initially designed to support
agriculture and increasingly utilized to support residential
development, has been a major cause of wetland decline.
3. IMPACT OF FEDERAL PROGRAMS
o Federal drainage and flood control projects which alter the
natural water regime have had the greatest impact on the
Everglades. The Federal Government has financed 80 percent of
the cost of constructing the Central and South Florida Flood
Control Project which provides drainage and flood control for
agriculture.
o Agricultural programs and incentives for residential
development have led to the filling of wetlands and increased
the pressure for Federal flood control and drainage efforts.
o Federal funds for highways and airports have helped to
establish the infrastructure for expanded residential
development.
4. AGRICULTURE PROGRAMS
o Federal agricultural programs prominent in the Everglades are:
construction of a system of secondary canals for farm
drainage; below market rate operating and ownership loans;
crop insurance at subsidized rates; price supports and import
restrictions for sugarcane; and citrus and dairy marketing
orders. /3/
o The Swampbuster provision of the Food Security Act of 1985, as
amended is almost completely ineffective in deterring the
conversion of wetlands to sugarcane, because the most
important subsidies for sugarcane (price supports passed
through sugar processors and import quotas on sugar) are not
among Swampbuster's sanctions.
5. URBAN DEVELOPMENT AND TRANSPORTATION PROGRAMS
o Tax deductibility of mortgage interest and property taxes,
mortgage insurance, flood insurance, and low interest loans
for expanding the supply of electricity are the principal
Federal programs that support residential development in the
Everglades.
o The Federal Government provides 90 percent of the funds for
Federal highway construction and 75 percent of the funds for
other roads.
6. RECOMMENDATIONS
o To protect the Everglades from further conversion and impaired
water quality, activities such as dredging, filling, and
subsidization that support existing development and foster new
growth would have to be restrained, and regulation of wetland
use would have to be more inclusive and vigorous.
o Tie Swampbuster requirements to price support loans and the
maintenance of marketing allotments for sugar. (Marketing
allotments are the amounts of sugar that any processor can
market within the U.S., and thus receive the artificially high
domestic price for sugar.)
o For almost a year, the Department has been negotiating with
the agricultural parties who have challenged the 1991
settlement agreement of the United States' suit of the State
for water quality violations. If these negotiations fail to
provide an acceptable arrangement for restoring water quality
to the Everglades, Congress should consider restructuring the
import quotas for sugar in order to promote a solution.
o Explore the possibility of denying Federal program benefits to
industries, regions, or States found in violation of water
pollution control standards.
o Consider having all Federal agencies assess the effects of
their programs on wetlands and, to the extent feasible,
minimize adverse impacts.
COASTAL LOUISIANA
1. DESCRIPTION AND IMPORTANCE
o Coastal Louisiana is heavily endowed with wetlands: 2.5
million acres of marshes (fresh, brackish, and saline) and
637,400 acres of forested wetlands. It contains about 40
percent of the coastal marshes in the coterminous United
States.
o This network of wetlands supports a fishery which accounts for
28 percent (by volume) of the total catch of U.S. fisheries.
It also provides winter habitat for one-half to two-thirds of
the Mississippi Flyway waterfowl population.
2. EXTENT OF THE LOSS
o Coastal Louisiana contained 4.07 million acres of wetlands at
the turn of the century. From 1900 to 1978 Coastal Louisiana
lost about 22 percent (901,200 acres) of its wetlands, with
3.17 million acres remaining in 1978. At least 300,000 acres
are estimated to have been lost since 1978.
o Louisiana loses approximately 35 to 37 square miles of coastal
wetlands annually. This is one of the Nation's most serious
wetland problems.
3. SOURCES OF LOSS
o A combination of natural and human factors have caused the
wetland decline.
o Natural factors contributing to the loss of wetlands include:
subsidence, erosion due to storms, and the rise in sea level.
/4/
o Historically, sediment deposition from the Mississippi River
worked to offset any losses and replenish the wetlands. In the
last century, however, dams and levees built along the
Mississippi River have altered this process, preventing
sediments from reaching the coastal plains.
o Approximately three-fourths of Louisiana's recent coastal
wetland loss takes the form of conversion to open water and is
attributable to subsidence, erosion, and canal dredging for
oil and gas pipelines. Human factors, particularly levee
construction along the Mississippi River, have accelerated
subsidence and erosion of wetlands. Other primary causes of
wetland loss include spoil disposal and conversion to
urban/industrial development. Agricultural drainage and
miscellaneous factors account for a small percentage of recent
coastal losses.
4. IMPACT OF FEDERAL PROGRAMS
o Flood control and navigation projects have been the major
cause of wetland loss in Louisiana. These projects have been
almost entirely federally financed.
o To a lesser extent, Federal hurricane protection and highway
projects have had an impact.
o A number of economic incentives offered by the Federal
Government have served to increase profits and led to
increased wetland conversion for: oil and gas development (tax
benefits in the form of oil and gas depletion allowances and
the expensing, as opposed to capitalizing, of intangible
drilling costs), urban growth (flood insurance, mortgage
insurance, low income housing, highway construction), and
agriculture (price supports, low interest loans, disaster
payments). The advent of Swampbuster has greatly diminished
agricultural losses, however, and compensatory mitigation is
routinely required for urban development in wetlands as a
condition for State and Federal permits.
o As a result of the Coastal Wetlands Planning, Protection, and
Restoration Act of 1990, a task force of State and Federal
agencies is preparing a comprehensive plan to address
Louisiana's problem with coastal wetland loss. The Act
provides for funding to implement wetland restoration projects
approved by the task force. Without aggressive action to
reverse the trend, the rate of loss of coastal wetlands in
Louisiana will doubtless continue.
5. RECOMMENDATIONS
o Proceed with construction of two authorized but uncompleted
water diversion projects: Lake Pontchartrain and Davis Pond.
These projects would restore a small percentage of the
freshwater and some sediment lost as a result of the
Mississippi River and Tributaries Project. They are an
essential first step in reducing the coastal losses.
o Consider expanding the Corps' Civil Works Program to protect,
create, restore, and enhance wetlands in Coastal Louisiana.
The Corps now has numerous authorities to construct or modify
projects to benefit wetlands.
o Evaluate the revenue and industry import of eliminating the
Federal income tax deductions in wetland areas for oil
depletion allowances granted to independent producers and for
intangible costs associated with drilling.
o Consider developing a performance-bond approach for the
mitigation of wetland losses. Under this approach,
environmental standards are established for permittees to
meet. Simultaneously, permittees must post performance bonds
sufficient to cover the cost of restoration, penalties, and
the Government's administrative costs in the event the
standards are not met.
o Consider establishing stronger mitigation requirements within
the regulatory programs, reflecting the quality and functional
values of affected wetlands. As a first step in the
implementation of the goal of no net loss of wetlands, the
Corps and EPA have begun to strengthen the mitigation program.
o Consider suspending Federal subsidization and support for
urban development in environmentally significant wetlands,
e.g., funds for low income housing, mortgage insurance, and
National Flood Insurance.
o Consider having all Federal agencies assess the effects of
their programs on wetlands and, to the extent feasible,
minimize adverse impacts.
GALVESTON BAY OF TEXAS
1. DESCRIPTION AND IMPORTANCE
o This region contains highly valuable marine resources and
habitat for waterfowl, and supports the most productive
commercial and sports fisheries on the Texas coast.
o The Bay's wetlands buffer inland areas from storm waves and
tidal surges and treat runoff waste from agricultural, urban,
and industrial sources.
2. EXTENT AND SOURCES OF LOSS AND DEGRADATION
o From the mid-1950s through the 1970s, the Galveston Bay area
lost about 1,110 acres annually to open water. The rate of
loss appears constant, except when exacerbated by hurricanes
or tropical storms.
o The cumulative loss and the rate of loss are significant.
However, the chief wetland problem in the region is water
quality degradation. Pollutants have exceeded the natural
assimilative capacity of the area, resulting in a decline in
the quality of wetlands.
o The key factors currently contributing to wetland decline are:
industrial development, including oil and gas development and
refining; urbanization; navigation channels; flood control and
multipurpose water projects; and pollution due to industrial,
urban, and agricultural runoff.
o The Galveston Bay Region is home to the largest petrochemical
capacity in the world and the most important supply of natural
gas in the nation. The attendant pollution has seriously
altered the wetlands.
o The Houston-Galveston area is one of the fastest growing
metropolitan areas in the U.S. Urban runoff adds significantly
to wetland loss and functional degradation in the area.
o Agriculture based on rice and cattle accounted for most of the
early loss of the region's wetlands. Although agriculture's
influence has diminished, farm runoff and nonpoint discharges
together with an altered hydrology due to farm drainage
ditches continue to affect these wetlands.
3. IMPACT OF FEDERAL PROGRAMS
o The major Federal construction activities that impair the
area's wetlands stem from multipurpose flood control and
navigation projects. These projects not only promote
development, but also concentrate and speed contaminants to
the bay system.
o The Federal Government provides incentives for urban
development that affects wetlands.
o Federal programs for constructing and providing technical
assistance for drainage ditches have destroyed wetlands in the
past, but no longer seem to have a major impact, as a result
of program changes in response to Executive Order 11990.
o Although industrial and urban development receive some impetus
from Federal funds, the major Federal activity influencing the
region's water quality is regulation. Protecting water quality
through the regulatory process presents many problems.
4. RECOMMENDATIONS
o Examine the current approach to the regulation of water
quality, particularly the National Pollution Discharge
Elimination System (NPDES), as it pertains to wetland impacts
and develop a more effective system of pollution control. In
many areas, degradation of water quality is an even more
serious problem than loss of wetland acreage. (See
recommendation 3 in Chapter 9 for specifics.)
o The Galveston Bay National Estuary Program is close to
completing a comprehensive study and management plan
addressing all Federal, State, and local programs affecting
the biological integrity of the Galveston Bay Estuary. All
Federal environmental evaluation documents (Environmental
Assessments and Environmental Impact Statements) should
disclose whether proposed projects are in compliance with the
forthcoming Comprehensive Conservation and Management Plan for
Galveston Bay.
o Have Federal agencies assess the effects of their programs on
wetlands. Where feasible, agencies should minimize the adverse
effects of their programs on wetlands. Where this proves
infeasible, agencies should be prepared to explain why it is
not feasible.
o Consider suspending Federal programs which subsidize or
support urban development projects that destroy wetlands,
e.g., funds for mortgage insurance and national flood
insurance. (A subsidy-free zone would correct market
distortions by such programs. The distortions add to
developmental pressures in these wetlands.)
o Encourage development of integrated crop management approaches
to agriculture. High levels of fertilization and pesticide use
can be reduced by making different technologies more readily
available.
PUERTO RICAN COAST /5/
1. DESCRIPTION AND IMPORTANCE
o Puerto Rico has several varieties of wetlands, but mangrove
forests, found along tropical and subtropical shores, are the
primary wetlands at risk.
o Mangroves serve several important functions, including: rapid
formation of biomass which helps to sustain life in nearby
marine environments; habitat for birds, fish and
invertebrates; and protection against erosion and wave damage,
particularly during tropical storms.
o Historically, estuaries covered 60,000 acres in Puerto Rico,
with about half of the area being mangroves. The most recent
estimate of mangroves in 1974 put the remaining acreage at
16,029 acres, about 53 percent of the original total.
2. IMPACT OF DEVELOPMENT
o In the past, mangrove and upland deforestation resulted from
the demand for fuel by households and large sugarcane mills.
Drainage for sugarcane and malaria control reduced wetlands in
the early 20th century. By the 1940s, canals, dikes, and pumps
had altered hydrological patterns.
o Programs aimed at transforming Puerto Rico from an agrarian to
an industrial economy had a significant impact on the region's
wetlands during the 1950s and 1960s.
o Economic development and housing projects, often justified as
a way to relieve the chronic 15 to 20 percent unemployment
rate, are the greatest threat to coastal wetlands. Development
pressure in the form of resorts, marinas, vacation homes,
housing projects, and industrial facilities has sharply
increased since 1985.
o Existing regulatory programs and pre-development consultation
policies have not stemmed construction in mangroves and
coastal wetlands. Abandoned projects and unoccupied buildings
attest to the poor planning that has occurred.
3. THE FEDERAL ROLE
o Federal economic incentives play a major role in promoting
development activities which affect Puerto Rico's wetlands.
o Most significant seem to be flood insurance, federally insured
home mortgages, and flood control projects, followed by
transportation projects, grants offered by the Economic
Development Administration, tax code provisions allowing the
deduction of interest on second homes, and income tax
exemptions for companies locating in the islands.
o Without this Federal support many of the development projects
would not have gone forward. Despite subsidies and numerous
Federal programs, the unemployment rate remains relatively
constant.
o The Corps' regulatory office in San Juan appears to be
understaffed to handle the case load, and penalties are
insufficient to serve as meaningful deterrents to continued
illegal fills. Further, the Environmental Protection Agency
office responsible for Puerto Rico is located in New York, and
is equally overburdened.
4. RECOMMENDATIONS
o Deny flood insurance and disaster assistance to communities
which do not enforce floodplain management ordinances.
o Revise the flood insurance program in Puerto Rico to take
account of the flood control capacity of wetlands and to
comply with the program's own regulations requiring protection
of mangroves in areas subject to high wave velocity.
o Strengthen the enforcement program of the Corps of Engineers
in response to illegal filling of wetlands.
o Consider amending the Coastal Barrier Resources Act to provide
for automatic inclusion in the Coastal Barrier Resources
System (CBRS) of "otherwise protected areas" whose protective
covenants are violated.
o Encourage HUD to require grant recipients to provide
documentation of coordination with resource and regulatory
agencies and of concurrence by these agencies that grant
recipients fulfilled their environmental responsibilities.
CALIFORNIA'S CENTRAL VALLEY
1. DESCRIPTION AND IMPORTANCE
o The wetlands of the Central Valley provide wintering habitat
for 19 percent of the wintering waterfowl in the continental
United States. They support some of the highest densities of
wintering waterfowl in the country. Nationally, they are the
highest priority wetlands for preservation of wintering
habitat.
o The Central Valley contains eight national wildlife refuges
and four State wildlife management areas, totalling 86,700
acres, much of which is wetlands.
o These wetlands help to maintain ecosystem productivity by
detaining and slowly releasing flood waters, recharging
aquifers, stabilizing shorelines, and filtering sediments and
pollutants from agricultural activities.
2. EXTENT OF LOSS
o In the mid 1800s, the Central Valley had an estimated 4.1 to 5
million acres of permanent, seasonal, and tidal wetlands,
including freshwater and brackish marshes and riparian areas.
o By 1939, Central Valley wetlands had been reduced to
approximately 619,000 acres. These losses preceded the
construction of the Central Valley Project. Losses were
primarily the result of agricultural activities, as well as
diking and levee construction in the Delta.
o In the mid-1980s, about 379,000 acres of wetlands existed in
the Central Valley, approximately six to nine percent of the
original complement. Few of these wetlands remained in their
natural state.
3. SOURCE OF LOSS
o The conversion of wetlands to agricultural lands accounts for
the loss of over 90 percent of the original wetlands in the
Central Valley. To a far lesser extent, these wetlands compete
with municipal and industrial development. The Fish and
Wildlife Service estimates that less than 0.8 percent of the
wetland losses in the Central Valley since 1939 were due to
urban development.
o In the Central Valley, there are 15 Federal and 25 State and
private dams with capacities of 75,000 acre-feet or more.
Water development and management (flood control, drainage,
irrigation, and storage for a variety of purposes) has
permitted the growth of an agricultural economy that accounts
for an estimated six percent (by value) of the Nation's
agricultural output.
o Water development and agricultural activity have altered the
remaining wetlands so that they, like agriculture, depend on
managed water regimes.
o Prior to passage of the Central Valley Project Improvement Act
of 1992 (CVPIA), publicly-held wetlands had no reliable source
of water of acceptable quality, delivered on a timely basis.
/6/ In many areas, wetland managers have come to rely on
irrigation drainwater to support wetland resources. Drainwater
is often contaminated with pesticides, leached salts, and
trace elements.
o Population in the Valley is expected to grow from 4.5 to 7.5
million by the year 2010. Increasingly, the region is
attracting new businesses and industries. Large numbers of
people are electing to live there and commute to work in the
Bay area. This growth competes with wetlands and other uses
for water.
4. IMPACT OF FEDERAL PROGRAMS
o The major Federal factors causing wetland decline in the
Central Valley have been subsidized water development (flood
control, drainage, storage, and distribution), technical
assistance, and research, along with farm price and income
support programs. /7/
o In the Central Valley, about 1.15 million acres which receive
federally subsidized water are planted in surplus crops like
rice and cotton.
o Among agriculture programs, the income and price support
programs have probably had the greatest impact on the
wetlands, but the legislative reforms in the 1985 and 1990
Farm Bills significantly reduced the influence of these
programs. The distorting effects from a number of other
agricultural programs (e.g., marketing orders) remain,
however.
o In the absence of water subsidies there would have been far
less agricultural development in the Valley.
o Historically, water development and agricultural programs have
been among the most important factors leading to wetland
decline, groundwater depletion, and degradation of the water
quality in the Central Valley.
o The CVPIA dramatically alters the way in which water and the
environment are managed in the Central Valley. The Act
institutes a number of water pricing reforms, establishing an
increasing block rate structure and imposing user fees to pay
for protection and restoration of the environment. The CVPIA
directs the Secretary to provide reliable, clean water
supplies to publicly owned wetlands and refuges, with water
deliveries growing over time to meet specified wetland
restoration and enhancement goals.
o The CVPIA will not solve all the wetland problems in the
Central Valley. The Act primarily addresses the water needs of
public-owned wetlands, which account for less than one-
fourth of the Valley's wetlands.
o The CVPIA also addresses the issue of drainwater contamination
by requiring that amended or renewed CVP contracts contain
provisions requiring contractors to comply with State and
Federal water quality standards for agricultural drainwater.
5. INEFFECTIVENESS OF SWAMPBUSTER
o Normally, in an area where participation rates in Federal
agricultural programs are high, one would expect Swampbuster
to significantly reduce the attractiveness of converting
wetlands to agriculture. This is not so in the Central Valley.
o Swampbuster is likely to be almost completely ineffective in
this region, because Sec. 1222(a) of the Food Security Act of
1985 provides an exemption for "artificial wetlands," and
almost all the remaining wetlands in the Central Valley fall
into this category.
6. RECOMMENDATIONS
o On future construction, eliminate the interest subsidy for
irrigation in Reclamation law, as well as the use of
hydropower revenues to repay a portion of irrigation capital
costs. The subsidies were designed to encourage settlement of
the arid west by small family farmers. Today the goal of
populating the west with small family farms is obsolete.
Consideration should be given to amending the law to reflect
changed social, economic, and environmental conditions.
o Consider charging persons who alter Central Valley wetlands
the full cost for water from the CVP.
WESTERN RIPARIAN WETLANDS
1. IMPORTANCE
o Western riparian areas and wetlands have great significance
for certain functions (such as wildlife habitat) because of
the arid climates in which they are found.
o They slow flood waters; aid in erosion control through
shoreline protection and dissipation of the energy force of
currents; trap sediments; and improve water quality by
filtering pollutants from upland sources.
2. EXTENT OF LOSS
o Nationwide, 60 to 75 percent of riparian wetlands have been
converted to other uses, whereas in the West estimates are
that some riparian areas have declined by as much as 90 to 95
percent.
o Surveys of the riparian areas remaining within western public
rangelands are incomplete, but thus far the evidence indicates
that most are not in healthy, fully functioning condition or
functioning, but vulnerable.
3. SOURCES OF LOSS AND DEGRADATION
o Poorly managed livestock grazing is among the leading factors
responsible for riparian wetland degradation in the West.
o Water projects (multipurpose reservoirs, small hydroelectric
projects, and small diversions for irrigation) are a leading
cause of riparian wetland loss. Both the construction of the
projects and the way in which they are managed and maintained
have significant effects on riparian areas.
o "Vegetation management" in connection with water projects
(mowing, burning, clearing, or spraying of plants in riparian
and upland areas) ranks behind grazing and water projects as a
factor responsible for western riparian wetland decline.
Historically, the practice was much more prevalent than it is
now. Vegetation management is conducted to maintain floodways,
expand pasture and cropland, and help control the Rio Grande
River in order to maintain a constant border between the
United States and Mexico. At one time vegetation management
was practiced extensively to conserve water for irrigation and
municipal use. Recent studies have cast doubt on the extent of
the water conservation benefits associated with vegetation
removal. As a result, the Bureau of Reclamation is not
currently using vegetation management to salvage water.
o Timber harvesting and associated road building as well as
mining and sand and gravel extraction affect wetland acreage
and water quality in the region.
4. IMPACT OF FEDERAL PROGRAMS
o Federal involvement accompanies each of the activities
discussed above: livestock grazing; water projects, such as
multipurpose dams built primarily for irrigating the arid
west; agricultural programs that subsidize certain crops;
small hydroelectric facilities; small diversion projects;
"vegetation management;" below-cost timber sales; and special
tax provisions for mining.
o Federal land management and water resources development
agencies have not adequately protected riparian areas because
of conflicting developmental responsibilities, e.g., grazing,
agricultural irrigation, electric power development, and
resource extraction.
o The grazing programs conducted by the Bureau of Land
Management (BLM) and Forest Service have been criticized for
exceeding the carrying capacity of some parts of the range,
especially in riparian wetlands.
o In 1988, the General Accounting Office (GAO) reported that
ranchers have generally resisted efforts to improve riparian
areas and have effectively opposed restrictions on their
livestock's access to riparian areas. GAO also noted a Federal
agency bias towards ranchers and against riparian area
protection at the management level (GAO/RCED-88-105).
o BLM has acknowledged deficiencies in its program. In order to
address these problems, BLM has adopted a formal riparian
policy, and has completed an analysis of the resources needed
to implement the new policy. The analysis provides a blueprint
for future riparian wetland management; it outlines goals,
strategies, and funding requirements. BLM has already begun
implementation of its new policy, and has set a goal of
restoring 75 percent of the riparian wetland areas under its
jurisdiction to proper functioning condition by 1997.
o The Forest Service is implementing a national strategy for
protecting, restoring, and managing riparian ecosystems, as
well. The program includes the assessment of ripanian
condition, modification of existing Land and Resource
Management Plans, and restoration of the riparian functions
and values throughout the Nation Forest System.
o As one of its principal resource management initiatives, the
Administration intends to make major revisions to regulations
and policies governing rangeland management. The Department
anticipates publishing proposed rules in 1994. Principal items
addressed in the proposed rule are: increasing the grazing
fee; incorporating newly developed stewardship
responsibilities as terms and conditions of all permits and
leases; making an applicant's history of compliance with
grazing statutes and rules a paramount consideration for
renewal of permits or granting of new leases; imposing a
surcharge on revenues from subleasing; and providing for
expeditious enforcement of field manager decisions regarding
violators.
o The Bureau of Reclamation, the Corps of Engineers, the
International Boundary and Water Commission (IBWC), and the
Soil Conservation Service all construct multipurpose water
projects that alter water regimes and produce major changes in
water flows that affect riparian areas and the species that
depend upon them. Although there has been modest improvement
in recent years in the manner in which these projects are
financed, they remain heavily subsidized.
o Subsidized irrigation water is used to grow crops that are
eligible for Federal agricultural subsidies, including price
and income supports. The production of wool and mohair is also
subsidized with price and income supports.
o The Bureau of Reclamation, the Corps, the IBWC, and the
Agricultural Stabilization and Conservation Service (ASCS)
have all conducted extensive vegetation management programs.
The Bureau no longer engages in this activity for water
conservation. The ASCS continues to subsidize vegetation
management on private lands; the Corps uses it to maintain the
water transport capacity of floodways; and the IBWC maintains
50,000 acres devoid of native vegetation in its efforts to
control the location of the Rio Grande.
o Because of the arid climates in which they are located,
Western riparian areas frequently have a proportionately
greater significance than wetlands and riparian areas
elsewhere in the United States. Yet riparian areas in the West
often do not qualify technically as wetlands for purposes
of regulation under section 404 of the Clean Water Act.
5. RECOMMENDATIONS
o Fund Federal water projects affecting wetlands in accordance
with the benefit principle of public finance, i.e., each
beneficiary should bear the cost (including interest costs and
any wetland opportunity costs) of generating his benefits.
o Consider eliminating Federal financial incentives for the
construction of small water diversion projects. The resulting
irrigation is a private activity; there are no public benefits
for which taxpayers should be responsible. Further, the
subsidy conflicts with other conservation goals, including
protection of riparian wetlands.
o Re-examine the use of Federal funds for "vegetation
management" associated with water projects.
o Consider having all Federal assistance programs comply with
the conservation, mitigation, and reporting requirements
contained in the Electric Consumers Protection Act (ECPA).
ECPA requires that a project: must not have significant
adverse effects on the environment; cannot adversely affect a
wild or scenic river; and must comply with recommendations
made by the resource protection agencies, or the sponsoring
agency must explain why this is not possible in terms of the
primary agency mission.
o As part of its technical review of wetland delineation issues
ask the National Academy of Sciences to examine the
feasibility of developing delineation procedures for western
riparian areas.
SOUTHEASTERN ALASKA
1. DESCRIPTION AND IMPORTANCE
o About 4.9 million acres (25 percent) of the 18 million acres
of land in Southeastern Alaska are classified as wetlands.
o The region is environmentally rich, containing: the Tongass
National Forest; 21,000 miles of tidal shoreline; over 2500
important anadromous fish streams, which support an
internationally renowned salmon fishery; and a wide variety of
wildlife.
2. EXTENT AND SOURCE OF LOSSES
o Urban development and logging are the principal sources of
wetland loss and functional degradation in the region. Wetland
effects of logging can result from clearcutting, construction
of logging roads, and the building and use of transfer sites
for transporting logs by waterways. Once vegetation
reestablishes itself in a logged area, there may not be any
reduction in wetland values, but in the interim erosion can
produce environmental effects.
o The direct loss of wetlands has been small. Only about 2300
acres of Southeastern Alaska's wetlands have disappeared as a
direct result of logging. However, the logging has produced
some erosion and subsequent siltation of wetlands and streams.
3. IMPACT OF FEDERAL PROGRAMS
o Large-scale logging in the Tongass began in the 1950s, when
the Forest Service attracted two companies with fifty-year
timber contracts. The principal output is pulp for shipment to
the Orient.
o The major incentives to log the Tongass stemmed from mandatory
harvesting provisions in the Alaska National Interest Lands
Conservation Act of 1980 (ANILCA) and the price-setting
policies utilized by the Forest Service.
o ANILCA stimulated logging by mandating that the Forest Service
make 4.5 billion board feet (bbf) available for sale and
harvest from the Tongass every decade. In 1990, Congress
passed the Tongass Timber Reform Act (TTRA) which rescinded
this mandate and ordered that competitive prices dictate the
level of harvesting.
o The TTRA ended the non-competitive nature of the pricing
practices on the Tongass, terminated some timbering subsidies,
and mandated that logging be conducted in a more
environmentally sound manner.
4. RECOMMENDATIONS
o FY94 appropriations for the Forest Service mandates a habitat
protection study for the Tongass National Forest. Depending
upon the results of this study, consider expanding the buffer-
zones (like those required in the Tongass Timber Reform Act)
to cover all streams which can affect the water quality of
anadromous fish habitat.
WESTERN ALASKA
1. DESCRIPTION AND IMPORTANCE
o The landscape of western Alaska is very diverse. It ranges
from the rugged fjords of Prince William Sound to the rolling,
treeless terrain of the Bering Sea coast, from the vast taiga
muskeg of the interior to the flat expanse of the tundra
underlain by permafrost that constitutes the Arctic coastal
plain.
o About 47 percent of an estimated 355 million acres of lands in
western Alaska is classified as wetlands.
2. EXTENT AND SOURCES OF LOSS
o The major causes of wetland loss in western Alaska are from
oil and gas development on the North Slope, placer mining
along the rivers and streams of the interior, and urban
development and development of transportation corridors.
o Less than one percent of the wetlands in western Alaska have
been lost as a direct result of oil and gas activities,
mining, and urban development.
3. IMPACT OF FEDERAL PROGRAMS
o Two provisions of the Federal tax code specific to the oil and
gas industry have helped to make development in Alaska more
lucrative: the oil and gas depletion allowance and the
expensing, as opposed to capitalizing, of intangible drilling
costs. Since 1975, only independent producers have been
eligible for the depletion allowance. There are very few
independents operating in Alaska. Further, oil development has
been so profitable in Alaska that neither of these tax
provisions is likely to have significantly altered the nature
of the industry or its impact on wetlands.
o To the extent that there is a subsidy to placer mining, it
derives from the absence of any fee for access to hard-rock
minerals on public lands. Largely through increased
enforcement efforts, placer mining operations in Alaska are
beginning to comply with water quality regulations.
o The Arctic National Wildlife Refuge (ANWR) is located just
east of Prudhoe Bay on the North Slope. The petroleum industry
has shown considerable interest in ANWR. In 1987, then
Secretary of the Interior Hodel recommended to Congress that
the coastal plain of ANWR be opened to full petroleum
exploration and development. Environmental organizations have
made the prevention of leasing and development in ANWR a
central feature of their agenda. The Administration is on
record as opposing leasing in ANWR.
4. RECOMMENDATIONS
o Consider having mine operators submit mining plans prior to
initiating mining activities. This allows resource managers
and regulatory authorities time to review plans, reduce
potential effects, and increase the likelihood of post-mining
reclamation.
o Consider developing a performance-bond approach for the
mitigation of wetland losses. Under this approach,
environmental standards are established for permittees to
meet. Simultaneously, permittees must post performance bonds
sufficient to cover the cost of restoration, penalties, and
the Government's administrative costs in the event the
standards are not met.
o Strengthen the mitigation requirements within the regulatory
programs to ensure adequate compensation for project impacts
to wetlands.
o Expand the joint industry-government efforts to develop more
effective methods for restoring and rehabilitating damaged and
functionally degraded wetlands. Recent cooperative efforts in
both the petroleum and mining industries have shown promise.
DELMARVA PENINSULA
1. DESCRIPTION AND IMPORTANCE
o The Delmarva Peninsula is bounded by the Delaware Bay and the
Atlantic Ocean on the east and the Chesapeake Bay on the west.
Due to the flat topography, runoff has been slow, forming a
rich network of wetlands connected by perennial or
intermittent streams.
o These wetlands intercept and filter agricultural runoff and
provide food and habitat for a great diversity of species.
2. EXTENT AND SOURCES OF LOSS
o Between the mid-1950s and the late 1970s, the average annual
wetland loss in Delaware was 1600 acres, in Maryland 1000
acres, and in Virginia 3000 acres.
o Inland wetland losses stem primarily from agricultural
activities. Drainage for agriculture and channelization of
streams to carry surface water to Chesapeake Bay tributaries
account for over two-thirds of the freshwater wetland losses.
Creation of stock ponds and filling for urban development
account for much of the rest.
o The loss of coastal wetlands is caused primarily by draining
and filling for urban development.
3. IMPACT OF FEDERAL PROGRAMS
o Federal agricultural programs have had a major impact on the
decline of inland wetlands and have promoted conversion of
shallow wetlands to ponds for migratory waterfowl and cattle.
Pond development is often conducted with State and/or Federal
financial and technical assistance.
o The Small Watershed Program (PL-566) has had the greatest
effect on the Peninsula. It provides technical assistance and
construction money to local watershed management groups for
small watershed protection, flood prevention, and agricultural
and nonagricultural water management projects. Improving
agricultural productivity on existing lands and creating
incentives for agricultural expansion have been among the
program's principal goals. Historically, this was accomplished
mainly by building drainage channels. The program has been
instrumental in changing the hydrologic regime and the ecology
of the region. Although the PL-566 program is evolving and
becoming more environmentally sensitive, it continues to be a
matter of concern in some areas, including Delmarva.
o Swampbuster may reduce some agricultural conversion. However,
much of Delmarva's cropland is devoted to corn for the poultry
industry. Poultry producers are often integrated operations
which grow their own corn and do not participate in the
commodity programs. The effectiveness of Swampbuster to
restrain wetland loss is diminished by the lack of
participation.
o Federally insured mortgages, tax deductions for second homes,
and flood insurance have offered indirect incentives to urban
development.
o The interaction between these Federal programs adds to the
cumulative wetland losses in the Delmarva area.
4. RECOMMENDATIONS
o Deauthorize the PL-566 small watershed projects authorized
before 1980 or substantially modify them to effect more
environmental sensitivity and mitigation. Small watershed
projects undertaken after 1980 are subject to much more
stringent environmental constraints.
o Eliminate Federal funding and technical assistance for the
conversion of freshwater or tidal wetlands to ponds for
waterfowl, sediment control, or cattle.
THE POCOSINS OF NORTH CAROLINA
1. DESCRIPTION AND IMPORTANCE
o Found in the southeastern Atlantic coastal plain, pocosins are
nutrient-poor, forested or shrub wetlands that evolved over
the past 10,000 years due to blocked drainage and peat
accumulation.
o These wetlands serve as the last refuge for many upland and
floodplain species requiring large blocks of habitat.
o They stabilize estuaries by controlling the rate of freshwater
flow, thereby regulating salinity. Much of the State's
commercial fishery depends on this estuarine regime.
2. EXTENT AND SOURCE OF LOSS
o Originally, North Carolina is estimated to have had 11.1
million acres of wetlands of which 2.5 million acres were
natural pocosins. As of the 1940s, about 90 percent of the
original acreage remained.
o Since the 1950s, forestry and drainage for agriculture have
caused a fairly steady decline. Between 1973 and 1983, North
Carolina lost 1.2 million acres of wetlands, and stood out
among all southeastern States with the highest net loss of
wetlands.
o By 1980, only about 695,000 acres (31 percent) of the original
2.5 million acres of pocosins remained in their natural state.
A third of the original acreage had been totally converted,
and 36 percent had been partially altered or was scheduled for
development by the owners.
3. STATUS AND PROSPECTS
o Intensive, softwood plantation forestry, peat mining, and
agriculture represent the major threats to North Carolina's
remaining freshwater and forested wetlands. The severity of
the threats depends largely on market conditions.
o The area has lost two-thirds of its wetlands and has numerous
government programs operating within its environs which
distort incentives in favor of conversion and development.
Nevertheless, the Pocosins is less threatened than most of the
other study areas examined in this report. This is due largely
to: market economic conditions which make conversion (at least
temporarily) unprofitable, legislative reforms in the 1985 and
1990 Farm Bills which significantly diminished the incentives
in Federal agricultural law to convert wetlands to cropland,
and a revitalized regulatory program.
o The current low price of oil has dampened the interest in
developing peat for methanol or for generating electricity.
However, demand is likely to change under certain conditions:
if prices for alternative fuels rise; air pollution
regulations increase the costs associated with power
generation from coal; the demand for farmland increases; or
the price of land with wet soils declines.
o The depressed agricultural economy has reduced wetland
conversions. However, commodity markets are cyclical, and the
eventual recovery will increase the pressure on wetlands.
o The forestry industry is also depressed, but long-term,
worldwide expectations are for a growing scarcity of wood and
increasing timber prices.
4. THE FEDERAL ROLE
o Federal economic incentives for forestry, agriculture, flood
control, peat mining and transportation have encouraged the
conversion of freshwater wetlands in North Carolina.
o Silviculture benefits from cost sharing and tax concessions
for replanting. Prior to the 1986 Tax Reform Act, 60 percent
of forestry capital gains were exempt from taxation. The 1986
Act eliminated this provision.
o Prior to 1985 and the advent of Swampbuster, the principal
agricultural benefits that affected wetlands in the region
were price and income supports, crop insurance, and low
interest production loans.
o Small watershed projects (multipurpose dams, stream
channelization, drainage, and flood control) directly altered
the region's hydrology and made conversions feasible.
o Incentives for peat mining include Government guarantees for
some uses of the product, federally sponsored research, and
special tax deductions.
o Wetland impacts have been systematically underestimated by
highway planners, and there has been less than complete
mitigation for the effects of highway construction. In an
effort to address the latter problem, the State has recently
funded a mitigation bank.
o The 404 program has had a turbulent history in the Pocosins
during the last decade, resulting in a disrupted and poorly
implemented program. Many wetlands were filled or
significantly altered without permits. Following judicial
action and administrative changes, the problems seem well on
the way toward resolution.
o Until recently, low participation in agricultural programs
limited Swampbuster's effectiveness. The nature of farming in
the Pocosins has changed dramatically in recent years,
however, and as a result, Swampbuster's effectiveness should
increase.
5. RECOMMENDATIONS
o A number of Federal subsidies and tax concessions for
forestry, agriculture, peat mining, and water resource
projects were identified as affecting wetlands in the
Pocosins. Consider restricting these subsidies and tax
concessions where the development results in wetland
destruction. (See recommendations section of chapter 16 for
specifics.)
o Establish a uniform Federal mitigation policy, ensuring
adequate compensation for unavoidable adverse project impacts
on wetlands and acknowledging the quality and functional value
of the affected wetlands. The Corps and EPA issued a
Memorandum of Agreement on Mitigation for the 404 program in
February, 1990. The Corps/EPA guidelines serve as a starting
point for a Federal policy. Consider expanding the use of
performance-bonds in the wetland regulatory program.
NORTHEASTERN NEW JERSEY
1. DESCRIPTION AND IMPORTANCE
o In an area subject to severe flooding, the region's wetlands
serve as natural storage areas.
o The wetlands filter pollutants from urban runoff that might
otherwise enter aquifers and surface waters which supply
drinking water.
o These wetlands offer habitat for wildlife and migratory
waterfowl in a region where habitat is increasingly scarce.
2. EXTENT AND SOURCES OF LOSS
o The original acreage is known to be much larger than the
present stock, but historic data are too incomplete for an
accurate estimate. 1n 1976, there were 69,173 acres remaining
in the six-county study area.
o Agriculture posed the initial threat to wetlands in
Northeastern New Jersey. Subsequently, it was displaced by low
density housing and by highway, airport, landfill, and port
facility construction which often took place in wetland areas
away from population centers.
o Today, highway construction, commercial and industrial
building, higher density residential development, and flood
control efforts are the major activities affecting wetlands.
o The driving force behind current expansion is the growth of
the New York metropolitan area's population and economic
activity, as well as the propensity of some firms and
individuals to relocate at a distance from the crowded and
costly central city areas. The State of New Jersey is the most
densely populated in the country.
3. IMPACT OF FEDERAL PROGRAMS
o Federal financial support for highway construction and flood
control have made development technically feasible and less
costly and, as a result, have encouraged commercial and
residential growth.
o However, given Northeastern New Jersey's location on the
outskirts of the nation's largest metropolitan area, much of
the region's suburban development ultimately would have
occurred in the absence of Federal incentives. The Federal
incentives expedited the growth.
4. RECOMMENDATIONS
o Finance new Federal flood control and Federal-aid highway
projects in a manner that reflects the distribution of
benefits between regional and national interests.
o Consider requiring that a mitigation plan accompany proposals
for the authorization of new projects. To the extent
practicable, all Federal agencies should mitigate fully and
concurrently for wetland alterations stemming from
construction of Federal or federally supported facilities.
o Acquire critically important and vulnerable wetland complexes
either by direct purchase of land or easements or by cost
sharing with the State of New Jersey or local municipalities.
Although this region's wetlands serve a number of functions,
most critical economically is the flood control benefits
derived from undeveloped wetlands. A long-term wetland
acquisition plan should be undertaken as a primary aspect of a
coordinated flood control program.
MICHIGAN'S COASTAL WETLANDS
1. DESCRIPTION AND IMPORTANCE
o Michigan's mainland coastal shoreline stretches for 2300
miles; coastal island shorelines add another 1000 miles. The
coastal wetlands are found at river mouths, in sheltered bays,
along shallow shorelines, and behind barrier beaches.
o These wetlands offer habitat for wildlife and birds and are an
important source of recreation.
2. EXTENT AND SOURCES OF LOSS
o The original coastal wetland acreage is unknown. Currently,
the onshore coastal wetlands and the offshore vegetated
wetlands each cover a little over 100,000 acres.
o A study of five representative areas revealed an average
coastal wetland loss of 59 percent between 1900 and the mid-
1970s. Losses ranged from 50 percent to 77 percent in the five
selected areas.
o Early losses were due to drainage for agriculture and
mosquito control. Today, a host of activities related to
urban development are responsible for the loss. Residential
development is the most important factor. Other factors
include construction of highways, flood control structures,
recreational facilities (marinas, harbors, and boat launches),
navigation channels, and industrial sites. Upstream water
projects also have an impact on coastal wetlands.
3. IMPACT OF FEDERAL PROGRAMS
o Residential and recreational development constitute the
greatest threats to Michigan's coastal wetlands. There are
numerous Federal programs which subsidize these activities.
While the impact of each program is likely to be small, the
combination of Federal grants, loan guarantees, insurance, tax
incentives, infrastructure, and flood control programs may
have significant implications for coastal wetland areas.
o Regulatory programs are generally effective in controlling
large projects which individually would impose significant
environmental damage. The cumulative effects from numerous
smaller projects are not well-addressed, however.
4. RECOMMENDATIONS
o Have Federal agencies assess the effects of their programs on
wetlands. Where feasible, agencies should minimize the wetland
effects of their programs. Where this proves infeasible,
agencies should be prepared to explain why it is not feasible.
MICHIGAN'S NORTHERN FORESTED WETLANDS
1. DESCRIPTION AND IMPORTANCE
o Most of Michigan's forested wetlands are found in the upper
peninsula and the northern lower peninsula.
o These wetlands serve a variety of important functions,
including: providing habitat for many species; reducing flood
peaks within watersheds; acting as natural filters;
controlling erosion; and recharging and discharging
groundwater supplies.
2. EXTENT AND SOURCES OF LOSS
o The original acreage of forested wetlands in Northern
Michigan is unknown. Currently these wetlands total 3.3
million acres.
o Forest Service data indicate a 14 percent loss in Michigan's
forested wetlands between 1960 and 1980.
o In the late 1800s, these regions underwent heavy logging.
Since that time, the forests have regenerated.
o Attempts to clear and drain forested wetlands in the upper
peninsula for row and cash crop agriculture have proved
economically infeasible because of the short growing season,
poor soil quality, and an inability to achieve sufficient
drainage.
o Wood products companies are conducting drainage research in
the hope of making the area accessible to timber harvesting.
o In the future, peat mining and the development of vacation
homes could have an increasing impact on these wetlands.
3. IMPACT OF GOVERNMENT PROGRAMS
o The State Government promotes Michigan's forestry industry
through research, planning, technical assistance, worker
training, and property tax relief.
o The Federal Government offers low interest loans and cost
sharing for reforestation and a number of conservation
activities. Also, several provisions of the tax code allow
special expensing, rapid amortization, and investment credits
for forestry activities.
o Although the impact of these programs on the drainage of
forested wetlands is unknown, none of the programs has
conditioned eligibility on avoiding wetland effects.
4. RECOMMENDATIONS
o Have Federal agencies assess the effects of their programs on
wetlands. Where feasible, agencies should minimize the wetland
effects of their programs. Where this proves infeasible,
agencies should be prepared to explain why it is not feasible.
RAINWATER BASIN OF NEBRASKA
1. DESCRIPTION AND IMPORTANCE
o The Basin occupies about 4,200 square miles. An impervious,
clay subsoil resulted in perched water table and a dynamic
wetland complex of temporarily, seasonally, and semi-
permanently flooded wetlands.
o The Basin's wetlands provide spring, migratory habitat for
five to seven million ducks and geese, as well as breeding and
nesting habitat for resident shorebirds, waterfowl, and other
water-associated species.
2. EXTENT AND SOURCE OF LOSS
o Historically, nearly 4,000 individual wetlands occupied about
95,000 acres. Approximately 34,000 wetland acres remain, but
virtually all of these have been modified to some extent.
o Between the 1960s and the 1980s, shallower, more easily
drained wetlands declined by 74 percent, deep wetlands
declined by about 47 percent, and the intermediate wetlands
declined by 20 percent. These losses significantly altered the
composition of wetlands in the Basin.
o The loss of Rainwater Basin wetlands has forced water-
associated birds to concentrate in fewer wetlands. This
condition increases the incidence of disease and death. Since
1975, approximately 200,000 birds have died of avian cholera
in the Rainwater Basin, due at least in part to overcrowding.
/8/
o Most wetland conversion in the Basin has been to agriculture.
In addition, these wetlands are vulnerable to siltation and to
contamination by agricultural chemicals from adjacent cropland
and rangeland. Chemicals applied directly in irrigation water
concentrate in adjacent basins.
3. IMPACT OF FEDERAL PROGRAMS
o Much of the conversion in the Basin has been conducted with
Federal assistance through cost-sharing programs for water
management. Although these programs are now restricted, there
are some exceptions in the law. For example, cost-sharing and
technical assistance continue for soil and water conservation
measures, such as land leveling, terracing, and irrigation
water recovery systems. These measures can indirectly
contribute to wetland losses or degradation. No one exception
leads to a significant loss of wetlands, but collectively the
exceptions degrade and diminish the stock.
o The agricultural commodity programs (price and income
supports) have distorted market signals, and prior to the
advent of Swampbuster in 1985, induced the conversion of more
wetlands to agriculture than was economically efficient.
o In recent years, the farm program participation in Nebraska
has been high. Thus, if fully enforced, Swampbuster should
prove successful in discouraging wetland conversions in the
Basin.
o Collectively, the Federal subsidies have kept more land in
agricultural production than was efficient, and the runoff
from this land continues to degrade wetlands.
4. RECOMMENDATIONS
o Consider precluding the use of Federal financial and technical
assistance on any soil and water conservation project that
indirectly results in the destruction or functional
degradation of wetlands.
FOOTNOTES
/1/ The requirement for this report appeared first in the FY85
appropriations act for the Department of the Interior, but was
amended by the Emergency Wetlands Resources Act of 1986 (P.L. 99-645
section 402).
/2/ In 1988, the Environmental Monitoring and Assessment Program (EMAP) of the Environmental Protection Agency was initiated to provide improved information on the current status and long-term trends in the condition of the Nation's ecological resources. EMAP has a wetlands component. Its first interpretive report, describing the conditions of coastal wetlands, is scheduled for completion in 1996.
/3/ Marketing orders are Government-sanctioned rules between producers and handlers to establish production and commodity standards and exert an influence on market price. See discussion in chapter 7.
/4/ Of course, any future sea level rise may be due in part to global warming, and hence, related to human activity.
/5/ Although the text focuses on Puerto Rico, the problems and trends apply to the Virgin Islands, as well.
/6/ Most wetlands in the Central Valley are managed for wintering waterfowl habitat which requires a large volume of water in the late fall.
/7/ Widespread conversion of wetlands occurred in the Valley long before Federal water development. Farmers diked the floodplains for cultivation, but their efforts were only partly successful. The process of reclaiming the lands and developing the area took many years and required extensive Federal assistance.
/8/ R. G. Stutheit, Work Plan S-87, Mortality and Disease Investigations, W-15-R-44, Nebraska Game and Parks Commission, 1988.
END OF FOOTNOTES
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FEDERAL INCOME TAX CODE
The Tax Reform Act of 1986 repealed the investment tax credit that allowed agricultural investors to reduce their tax liabilities by 10 percent of the cost of sprinkler systems and other capital installations. The code now allows accelerated write-offs for certain "depreciable" property such as capital investments in irrigation. These investments are also subsidized by a special provision within Section 179 of the revenue code, which permits taxpayers to deduct as an ordinary business expense the first $10,000 of any investment. Irrigators commonly use accelerated depreciation and section 179 expensing for sizable investments such as sprinkler equipment, water well drilling, and ditch excavation, all of which can have negative effects on wetlands. In addition, certain irrigators may claim a special water depletion allowance. This deduction is available where an underground source is being pumped at an unsustainable rate. It enables an irrigator to compensate for a theoretical decline in property value that is presumed to go with the exhaustion of the water supply.
Collectively, these tax code provisions encourage groundwater overdraft. This is ironic, since one of the major reasons for dam construction in the arid West was to relieve pressure on the aquifers. Development of the surface water supplies was intended to alleviate groundwater depletion. /24/ Indeed, cheap surface water did replace groundwater in some service areas, but as the aquifers recovered, pumping for irrigation became technically and economically feasible elsewhere. /25/ Thus, in the absence of any regulation, groundwater depletion continues, although at a reduced rate.
FOOTNOTES
/24/ See CVP purposes in House Document No. 191, 73rd Congress, 1933 and House Document No. 416, Central Valley Project Documents, Part I, Authorizing Documents, 1956.
/25/ See Bertoldi, et al., 1991 for a discussion of groundwater problems in the Central Valley of California emanating from the hydrologic changes due to 1) development of groundwater for agricultural purposes and subsequent depletion of groundwater and 2) surface water development in relation to groundwater depletion.
END OF FOOTNOTES
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FEDERAL TAX PROGRAM
In addition to the effects of Federal programs, tax policies may
have the unintended effect of increasing the incentive to drain and
convert wetlands. Tax policies designed to stimulate agriculture,
capital investment, recreation, and timber production may increase
drainage and conversion or the modification of wetlands. By lowering
the cost of development to the landowner, these tax policies may
reduce costs and create incentives to develop more wetlands than
would have been developed in the absence of these policies.
The income tax code played a more significant role in decisions to convert and develop wetlands in the past than it does now. Changes instituted by the Tax Reform Act of 1986 (TRA) eliminated many economic incentives affecting wetlands. Arguably the most important of these changes occurred in the agricultural section of the code, where provisions which allowed expensing (rather than capitalizing) of conversion and development costs were eliminated. The elimination of the preferential tax rate for capital gains may have had a significant effect on forestry, because most timber sales qualified for capital gains treatment under prior law. As a result, a major advantage of holding forest land was eliminated, but the implications of this for wetland conservation is different in different areas, and the net result is not at all clear. The TRA did reduce the after-tax gains on sale of improved cropland converted from wetlands. /26/ In general, tax reform eliminated a number of special provisions which were designed to promote wetland conversion and development, while leaving unaltered the tax deductibility of expenses and depreciation incurred during the ordinary conduct of business activities which happen to affect wetlands. For a more detailed discussion of past tax provisions which affected wetlands and tax reform see Volume I of this report.
In addition to those provisions of the tax code which encourage development, there are also provisions which encourage conservation. The Federal tax code allows landowners who donate land or easements to qualified conservation organizations to deduct the value of the donation as a charitable contribution. By reducing tax rates, the TRA reduced the value of tax deductions. Limited evidence to date suggests that subsequent charitable contributions have fallen.
The Alternative Minimum Tax (AMT) may have had an even greater effect on conservation donations than the TRA. Under the AMT the marginal tax rate is 21 percent, considerably less than the top bracket (28 percent) under the ordinary income tax code. More importantly, however, until 1993, under the AMT the amount of a deduction for the charitable contribution of property was limited to the original purchase price of the property. Under the ordinary income tax code the fair market value of the property constitutes the value of the donation for purposes of tax deductibility. Thus, for wealthier taxpayers subject to the AMT, the tax savings resulting from a gift was significantly reduced. In the case of wetlands, this was important, because conservation donations tend to come from wealthier individuals. In the Revenue Reconciliation Act of 1993 (RRA), however, Congress eliminated the restriction on charitable giving imposed by the Tax Reform Act of 1986, and reinstated the full deductibility of contributions of appreciated property.
FOOTNOTE
/26/ Sec. 403 the Tax Reform Act specifically subjects the gains from sale of "converted wetlands" to ordinary income taxation rather than to capital gains tax treatment. This was done as a precaution, i.e., in the event that preferential tax treatment of capital gains is reinstated in the future, such preferential treatment will not automatically be extended to wetlands converted to agriculture. However, Sec. 403 does not apply to wetlands converted for any other purpose.
END OF FOOTNOTE
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USDA FOREST PROGRAMS
The Agricultural Stabilization and Conservation Service (ASCS) in conjunction with the Forest Service administers the Forestry Incentives Program (FIP), a cost-sharing program available to private, non-industrial landowners for forestry practices such as planting trees. This program was funded at $12.4 million in 1993. ASCS also administers the Agricultural Conservation Program which shares costs for various agricultural land conservation activities, including tree planting. The program was funded at $194.5 million in 1993, but the extent to which these funds were applied to forestry activities is not specified. The Federal Government will generally cover from 40 percent to 75 percent of allowed expenses. Often plantation trees rather than the mix of native species are planted, thus altering the original environment.
The Farmer's Home Administration (FmHA) aids the forest industry by offering: farm ownership loans to buy or develop forest land; refinancing of forest land, soil, and water loans for improving forest resources; and operating loans to help with normal costs of producing, harvesting, and processing forest products. Previously, these loans could be used to cover drainage costs, but if properly enforced, Swampbuster should preclude that. The 1985 Food Security Act included a new feature that, at the Secretary's discretion, allows delinquent farmers to reamortize loans and delay repayment if they plant at least 50 acres of softwood timber. This feature also offers an incentive to replace native hardwoods with softwood plantations.
FEDERAL INCOME TAX CODE PROVISIONS RELATED TO FORESTRY
Several provisions in the Federal income tax code allow special expensing, rapid amortization, and investment credits for forestry activities. Reforestation expenditures up to $10,000 for site preparation, seed or seedlings, tools, and labor are eligible for a 10 percent tax credit and may be amortized over only 7 years. It is not known how great an impact these programs have on the drainage of forested wetlands. However, if it proved significant, consideration might be given to conditioning eligibility for these provisions on avoidance of wetland conversion or degradation.
TIMBER PRODUCT EXPORT ASSISTANCE
Several export programs can be used for timber products, but no special timber export assistance programs exist. In general, timber products are included as agricultural commodities, and as such qualify for and are included in agricultural export assistance programs. Data on assistance for timber export are not reported separately from assistance for other agricultural commodity exports. It is not clear whether these programs are a significant factor in promoting the substantial exports of timber products to Japan from Northeast Alaska, but, if so, they could be implicated in some wetland loss and more importantly, some wetland degradation.
BUREAU OF LAND MANAGEMENT AND FOREST SERVICE GRAZING POLICY
In 11 western States, /6/ 48 percent of the land is federally owned and about 75 percent of that is grazed by domestic livestock. Thus, federally-permitted grazing occurs on 36 percent of the land in these States. In 1990, there were approximately 17 million beef cattle and 102,800 beef producers in 11 western States. About 18 percent of the producers had Federal grazing permits. In some of these States the percentage is much higher.
Both the Forest Service and the BLM administer livestock grazing programs on the lands that they manage. Together they administer 87 percent of the Government's rangeland.
The BLM and the Forest Service regulate grazing on public lands by granting 10-year permits or leases that specify the number of animal unit months (AUMs) of grazing allowed each season on a particular tract (called an allotment). The grazing program has been criticized for exceeding the carrying capacity on some parts of the range, especially in riparian wetlands.
FOOTNOTE
/6/ Arizona, California, Colorado, Idaho, Montana, Nevada, New Mexico, Oregon, Utah, Washington, and Wyoming.
END OF FOOTNOTE
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INCOME TAX CODE PROVISIONS RELATED TO THE OIL AND GAS INDUSTRY
The oil and gas production from wetland areas represents a significant amount of the energy used in the United States. Two special tax incentives are available to the oil and gas industry: the deduction for intangible drilling costs and the percentage depletion allowance, the latter benefit having been greatly reduced in recent years. The deduction for intangible drilling costs, allowing rapid write-offs of expenses related to oil and gas production, was introduced into the tax code through a series of administrative rulings by the Treasury Department, and then sanctioned by Congress in 1954. The deduction allows the owner to take an immediate tax deduction for "intangible" expenses -- labor, fuel, power, material, supplies, and tools -- associated with drilling and preparing an oil or gas well for pumping. The deduction was not available for "tangible" costs such as expenditures for pipe, tanks, and pumps used in an oil or gas rig. For most other types of construction projects, intangible costs can be deducted, but they have to be spread over the number of years that the facility will be used. In contrast, a full deduction can be taken for intangible drilling costs in the year the expenditures are made. This tax code provision is thought to be a significant factor in offsetting the costs of canal dredging and access road construction in Louisiana and pipeline construction in Alaska.
In 1926, Congress enacted percentage depletion to establish a rule-of-thumb measure for depreciation in the value of a well as its oil or gas is pumped out. Investment in the resource was considered to be a capital investment. The depletion allowance was arbitrarily set at 27.5 percent of production. The allowance bore no relation to actual costs and permitted tax-free recovery that in some cases vastly exceeded the amount invested in the property. Producers were allowed to deduct 27.5 percent of gross income from taxable income, with a limit on the deduction equal to 50 percent of taxable income.
In 1969, tax reform cut the oil and gas depletion allowance to 22 percent. In 1975, the depletion allowance was discontinued for all but independent producers. The reform phased in a lowered allowance for independents, leaving it at a permanent level of 15 percent by 1984 for the first 1000 barrels of oil and the first 6 million cubic feet of gas produced daily. These measures greatly reduced economic incentives to engage in marginal oil and gas exploration and production. The depletion allowance for independents may promote wetland loss in coastal Louisiana.
The Tax Reform Act of 1986 further diminished the tax incentives associated with oil and gas exploration and production by limiting both the percentage depletion allowance and the expensing of intangible drilling costs for purpose of calculating the alternative minimum tax. However, amendments to the tax code in 1992 granted relief from this provision to independent producers.
DEPARTMENT OF ENERGY PROGRAMS RELATED TO PEAT MINING
The Federal Government promotes the mining of peat for energy by guaranteeing a market and by conducting research. The Public Utilities Regulatory Policies Act of 1978 (PURPA) requires that public utilities purchase power from small producers at the utilities' own generation costs. This significantly reduces the risk associated with a new economic venture. The Government sponsored millions of dollars of research from the mid-1970s through the early 1980s on peat energy demonstration projects.
INCOME TAX CODE PROVISIONS RELATED TO PEAT MINING
Because peat is an alternative fuel in the pre-commercial stage, major research, development, and construction cost savings derive from special tax incentives. Of particular importance are those incentives that give peat mining a relative advantage over more traditional energy sources. Peat mining along with other alternative energy sources, for example, qualifies for accelerated depreciation of investment costs. Peat also qualifies for a five percent depletion allowance, a deduction from taxable income related to extraction levels that more conventional energy sources no longer receive. Peat may profit, too, from research and development credits. These are available for selected basic research expenditures and, because traditional energy technology is more developed, the credits will probably benefit peat and alternative energy disproportionately.
MINING LAW GOVERNING PLACER MINING
Placer mining (mining for minerals which have been deposited by stream action, often in a stream bed) has a long history of causing adverse impacts to fish and wildlife and their habitats in Alaska. Under the Mining Law of 1872, no fee is charged to miners for access to hard-rock minerals on designated Federal lands. Originally the Act covered oil and gas as well as hard-rock minerals. Now however, coal, oil, and gas are subject to leasing arrangements that require a fair price to be paid for public resources.
In 1990, hardrock minerals worth at least $1.2 billion were extracted from Federal lands. The known, economically recoverable reserves of hardrock minerals on Federal lands were estimated to be worth $64.9 billion (GAO 1992).
A mining company must stake a claim to secure a deposit against others. Although a claim may not exceed 160 acres, a mining company may stake an unlimited number of claims. A claim may be kept indefinitely so long as at least $100 of work is conducted on it annually and the company files an annual notice of work performed. Should a mining company wish to purchase the surface rights as well (a procedure known as patenting a claim), it may do so by demonstrating to the Government the existence of a mineral deposit that can be produced with a reasonable prospect of being profitable and paying a fee of $2.50 to $5.00 per acre, depending on the type of claim. However, the expense of developing the necessary geologic, engineering, and economic data often discourages companies from patenting claims.
- AuthorsBabbitt, Bruce
- Institutional AuthorsU.S. Department of the Interior
- Cross-ReferenceTax-related excerpts of the Interior Department's report will be
- Code Sections
- Subject Area/Tax Topics
- Index Termsoil and gas taxationAMTagriculture, conservationtimber, reforestation amortizationtimber, reforestation creditgain or loss, timbercapital gains, tax preference
- Jurisdictions
- LanguageEnglish
- Tax Analysts Document NumberDoc 94-6509 (348 pages)
- Tax Analysts Electronic Citation94 TNT 136-38