Conservation Compliance:
Policy Issues for the 1995 Farm Bill
Jeffrey Zinn
Senior Analyst in Natural Resources Policy
Environment and Natural Resources Policy Division
December 19, 1994
95-6 ENR
SUMMARY
Under provisions enacted in the 1985 Food Security Act, all
farmers producing agricultural commodities on highly erodible
land must fully implement an approved conservation plan by
January 1, 1995 to remain eligible for certain farm program
benefits. Conservation compliance to control erosion affects
about 140 million acres, more than a third of the country's
cropland. As the deadline approaches and the 1995 farm bill
debate begins, three questions will likely be raised. First, how
much erosion control is enough? Second, is USDA's enforcement
adequate? Third, will this approach become increasingly
ineffective if farm programs continue to be scaled back? This
paper reviews the compliance concept, the conservation compliance
requirements, the implementation record, and these three
questions.
BACKGROUND
The Concept
From their inception in the 1930s, and until compliance was
enacted in the 1985 farm bill, all soil and water conservation
programs offered through the agencies of the U.S. Department of
Agriculture (USDA) had been based on two principles: voluntary
participation and incentives. These incentives included technical
assistance (conservation planning and engineering) through the
Natural Resources Conservation Service (NRCS, formerly the Soil
Conservation Service), cost-sharing payments through the
Agricultural Stabilization and Conservation Service (ASCS),
education through the Extension Service (ES), and loans through
the Farmers Home Administration (FmHA). (Under the
recently-enacted USDA reorganization legislation, P.L. 103-354,
many of the cost-sharing programs are being moved to the NRCS,
and the ASCS and FmHA will be incorporated into the newly created
Consolidated Farm Services Agency). Employees of each agency are
located in most counties, providing easy access for most farmers.
However, in the late 1970s and early 1980s, as farm program
costs soared and substantial erosion problems were widely
reported, opinion surveys showed a growing portion of the general
public, and even the farm community, supported the idea that
farmers who receive Federal assistance should be required to meet
societal standards for environmental quality. This was a
significant change from the earlier prevailing view that
agriculture was an unique industry. Agriculture generally had
been exempted from requirements that applied to other business
and industrial sectors, such as many of the programs enacted in
the 1972 Clean Water Act.
Conservation compliance for erosion sets an environmental
standard for agricultural activities. When this and two other
compliance proposals surfaced in the 1985 farm bill debate, they
were quickly identified as a major shift in policy. (The others
set standards for highly erodible land that had not been
cultivated between 1981 and 1985 (sodbuster), and for wetlands
converted to agricultural uses (swampbuster).)
Supporters and opponents alike thought that compliance
proposals would be contentious. Many veterans of farm policy
debates did not expect compliance proposals to survive the
omnibus farm legislation deliberations. Supporters of compliance
reportedly were concerned that verbal support for the concept of
compliance would not translate to votes to enact legislation that
would significantly redirect conservation policy.
However, these compliance provisions were enacted after
surprisingly little discussion or debate. Policy analysts suggest
that earlier debate over sodbuster and discussion of "cross
compliance" in the 1982 National Conservation Program had
exposed this concept to congressional consideration, and probably
helped prepare the way for acceptance of conservation compliance
(and swampbuster).
Some opponents of compliance maintain that it has changed NRCS
from a farm-conservation support agency into a regulatory agency.
Compliance-program supporters counter that there have always been
requirements on program participants; compliance creates
additional requirements, not new regulations. Further, each
producer can still decide whether to be in or out of compliance,
and those who choose to be out of compliance still have full
market access. This debate--which has both philosophic and
practical dimensions--continues, and is concentrated in areas
where meeting the standards of compliance are especially
difficult or costly.
If compliance is viewed as a "stick" approach,
Congress also enacted a counterbalancing "carrot"
program in the same 1985 law, the Conservation Reserve Program
(CRP). CRP allows producers to retire highly erodible or
environmentally sensitive land under 10-year contracts. These
contracts start to expire in 1995. Compliance and CRP are
connected; at the end of the contract, the 75 percent of the 36.5
million acres in the CRP that meets the eligibility requirements
will be subject to compliance. These producers will have 2 years
after their CRP contracts expire to be fully in compliance if
crop production is resumed. (For more information on CRP, see CRS
Report 94-413, Conservation Reserve Program: Status and Issues.)
Conservation Compliance, as Amended
Compliance was enacted in 1985 and amended in 1990. Under the
1985 Food Security Act, farmers who cultivate highly erodible
lands must have an approved conservation plan by 1990 and have it
fully implemented by 1995. Producers who are out of compliance
lose eligibility for several farm support programs on all the
land the producer cultivates:
price supports and related programs;
farm storage facility loans;
crop insurance;
disaster payments;
storage payments; and
any FmHA loans that will contribute to erosion on
highly erodible lands.
The program was amended in several significant ways in the
Food, Agriculture, Conservation, and Trade Act of 1990.
Compliance was expanded to include highly erodible land set
aside, or taken out of production, under commodity programs. This
Act added six more Federal farm programs to the list of benefits
that could be lost for non-compliance. A graduated penalty was
added so that under some circumstances, producers could be
subject to only $500 to $5000 loss in benefits. This graduated
sanction is available only once every 5 years. The revisions
protect tenant farmers who may be ruled out of compliance because
of the actions of other tenants or the landowner.
Implementation
Implementation is shared by several agencies. CFSA administers
the conservation compliance provisions. NRCS is the lead
technical agency; it works with producers to develop and
implement conservation plans, and also field checks a sample of
the 1.6 million plans each year. Based on these checks, NRCS
passes along the names of those found not to be "actively
applying" their plans or not using an approved conservation
system to the appropriate administering agencies; these agencies
determine whether benefits will be lost. Producers can appeal a
non-compliance determination.
Compliance requirements have placed substantial pressures on
the NRCS staff. One source of these pressures has been the
increased workload. Compliance required that the new plans be
completed on approximately 140 million acres by 1990. (In
contrast, in 1984, the year before compliance was enacted, NRCS
assisted with plans on about 2.5 million acres.) NRCS completed
this task, using some new approaches. Since 1990, implementation
continues to place demands on NRCS staff as producers work toward
full implementation by 1995. Changes in farming techniques and
crops, incorporating new technology, and changes in ownership and
tenancy have contributed to revisions of almost half the plans at
least once. NRCS expenditures to implement compliance have
totaled $1.77 billion, or about $1,000 per plan.
A second source of pressure is the requirement to work with a
large number of new, and sometimes, less cooperative clients.
Many of the producers required to have compliance plans had never
chosen to work with NRCS in the past and viewed the requirement
as coercive. This view point has made farmer implementation more
difficult, and caused many in the agriculture community to view
NRCS as a regulatory agency.
In May 1992 and August 1994, the House Agriculture Committee's
Subcommittee on Environment, Credit, and Rural Development held
hearings to learn about the status of compliance. At the August
1994 hearing, USDA presented data based on a 1993 survey of 2.6
percent of all tracts subject to compliance. This data showed
that almost 50 percent of all the plans had been fully
implemented and another 42 percent were being actively applied.
But most of the remaining ones were the more difficult or
expensive plans. For example, in southwestern Iowa, where
terracing is required in many of the conservation plans, it was
not clear in 1993 that there was enough construction equipment
available to complete all the remaining terraces by the 1995
deadline, even if funds were adequate and all producers intended
to meet the deadline.
Current program criticisms center on adequate enforcement.
According to CFSA statistics, 1,944 producers were found to be in
violation of conservation compliance (and sodbuster) through
1992. The affected land area was just under 151,000 acres, and
benefits lost totaled almost $7.3 million. Critics believe that
this record shows lax enforcement, considering the billions of
dollars spent in commodity and other programs during the same
time period. Supporters of the current program point out that
NRCS concentrated its efforts on assisting farmers achieve and
retain compliance. Additionally, a very large majority of farmers
continue to progress toward successful implementation. The data
also show that the number of identified violators has increased
each year.
Data from the 1993 USDA survey shows that 3.6 percent of the
producers were out of compliance. Several States were in 100
percent compliance; States with less than 85 percent compliance
included Iowa (77 percent, Delaware, 80 percent; Vermont, 82
percent; and North Carolina, 84 percent). The Environmental
Working Group (EWG), an environmental think tank, analyzed USDA
data and found that only about 75 percent were fully applying or
actively applying their conservation plans. This battle over what
is meant by being in compliance, and what portion of all
producers are not in compliance is likely to continue.
POLICY ISSUES IN THE 1995 FARM BILLS
How Much Erosion Control is Enough?
Deciding how far erosion would have to be reduced to be in
compliance has been controversial. Initially the Department
stated that it would require producers to limit erosion to T, or
2T under some circumstances. (The T value is the theoretical rate
at which soil can be lost while still maintaining long-term
productivity. It varies with soil type from 5 to 2 tons
per acre per year.)
The final rule issued in 1988 added "economic and
technical feasibility" to this requirement to give producers
greater flexibility. It also allowed the use of "alternative
conservation systems" which might not reduce erosion to the
T level, but provide a great savings to the producer.
Subsequently, SCS Chief Scaling mandated that alternative
conservation systems be made available in all counties. This
upset environmental interests who felt that these alternatives
should be available only in very limited circumstances.
The continued use of alternative conservation systems may be
debated in the 1995 farm bill. Environmentalists would argue that
use of alternative systems is generally inappropriate, and that
producers should be held to the higher standard that Congress
intended in 1985. Strict adherence to those legislative
instructions would require many plans to be amended. Moreover, a
larger portion of the implementing activities would involve
conservation measures that need to be designed, built, and
maintained. Debate over the continued use of alternative
conservation systems is likely to revolve around being able to
clearly define whether and where they remain appropriate, and
around an ability to compare the costs of meeting more stringent
conservation requirements with benefits, both on the farm and off
it.
Is Enforcement Adequate?
As the 1995 deadline for full implementation approaches, some
producers continue to express concern about losing their
benefits. In the early years of compliance, some producers
thought that either Congress would extend the deadline, or that
compliance for erosion would be repealed. In the largest study of
producer views on compliance, the Soil and Water Conservation
Society found that more than half those surveyed between 1989 and
1991 did not expect to lose benefits if they were not actively
applying their conservation plans in 1995. These expectations
have not been matched by actions at USDA or in Congress. For
example, during the 1990 farm bill debate, Congress never
seriously considered extending or repealing the program. Some
producers will probably try to apply greater pressure for delay
under some circumstances, basing their arguments on a need for
being reasonable under difficult conditions.
Views vary on how the Department and its agencies are
enforcing compliance. Many environmentalists believe that NRCS's
field staff do not have the resolve to vigorously enforce
compliance, and point to the data compiled by the Environmental
Working Group (EWG). The Department has responded that
enforcement will gradually increase as the 1995 deadline
approaches. Enforcement data, especially in the early years, also
show that a high portion of those out of compliance were
concentrated in a few areas, indicating potential
inconsistencies. NRCS states that it is taking action to improve
consistency. EWG analysis indicates that the "not actively
applying" situations are increasingly concentrated--in 1993,
82 percent of those producers were situated in only 11 percent of
the counties. Viewed another way, only 19 counties had producers
lose more than $10,000 in benefits in 1991 and 1992 because of
compliance (and sodbuster) violations. Agricultural interests
would like to see both consistency and some flexibility,
especially in areas where there are practical problems, such as
not enough cost-sharing funds to support the necessary
improvements.
About 75 percent of the plans reportedly rely on residue
management. The effects of variable growing conditions from year
to year mean that producers have to build in a substantial margin
for years when residue is limited, such as a year after drought
conditions, or otherwise seek variances. This may be a
significant problem at locations where moisture is highly
variable from year to year. Basic questions that need to be
addressed include: what are the options to residue management?
where should they be used? and can they be adopted rapidly as
amendments to plans that depend on residue management? Some
producers may find that they must update their plans, requiring
more work for them and for NRCS, and generating possibly greater
producer dissatisfaction with the program.
NRCS has identified available agency resources as a potential
problem as the deadline approaches. Demand for services will
probably grow as producers increasingly believe that compliance
will not be delayed and flexibility will be minimal. The
anticipated increase in out-of-compliance determinations will
place further demands on staff to deal with appeals. Further
hampering implementation will be insufficient cost-sharing funds,
and finding more funds will be difficult. Finally, NRCS
downsizing will mean that less staff are available to administer
this program.
Will Other Changes in Farm Policy Affect the Compliance
Approach?
The future of compliance will also be viewed within the
context of more general trends in farm policy. If farm policy
continues to evolve away from large commodity programs and toward
greater reliance on producer decisionmaking and the marketplace,
then compliance may become increasingly irrelevant to a growing
portion of producers. This general trend is likely to be
reinforced by Federal budget constraints, by views about the
Government's role in the economy, and by changes in the makeup of
the 104th Congress. If farm support programs are cut back
significantly, some producers could decide to avoid farm program
participation and thereby avoid compliance. Thus, compliance
could become a less effective policy tool for conservation.
Supporters of the program's underlying goals may seek new
approaches to supplement compliance by limiting the potential for
unacceptable levels of soil erosion in future years. No new ideas
have been suggested as yet. Many in the agriculture community say
that they hope to avoid greater regulation and to rely on a
program driven by incentives. They believe that the overwhelming
number of producers desire agriculture that is not only
profitable, but environmentally positive. Other related
environmental legislation such as water quality and other
possible environmental benefits of compliance, which have not
been part of the debate up to now, may also emerge in 1995 as
Congress considers omnibus farm legislation.
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