overview
Incentive payments for natural resource conservation are a growing
part of farm and conservation policy. The Environmental Quality
Incentives Program (EQIP) provides technical, financial, and educational
assistance for a wide range of agri-environmental activities. EQIP
is attractive to producers because of the program's flexibility
in addressing natural resource concerns, while maintaining land
in productive agricultural use. EQIP applications have far exceeded
available funding. The increasing concern about environmental impacts
of working farm land, combined with high demand for EQIP funding
and the fact that financial support under EQIP is not constrained
by WTO rules, may increase EQIP funds available.
EQIP's principal objective, as enacted in the 1996 Farm Act, is
to achieve the greatest possible environmental benefits per dollar
of program expenditure. The program relies on a bidding framework
whereby farmers propose a cost-share level for the practices they
intend to undertake as part of a conservation plan. Environmental
targeting is accomplished by assisting farmers to implement a conservation
plan to address the identified priority resource concerns, explaining
what changes in farming practices are expected. A conservation plan
may include a combination of structural, vegetative, and land management
practices.
EQIP consolidates and better targets the functions of the Agricultural
Conservation Program (ACP), the Water Quality Incentives Program
(WQIP), the Great Plains Conservation Program (GPCP), and the Colorado
River Basin Salinity Control Program. EQIP's status as USDA's primary
conservation program providing support on working farm land, along
with the choice of among some 250 eligible conservation practices,
offers a unique opportunity for better understanding what conservation
practices are being implemented, how producers' conservation needs
vary regionally, and the costs of implementing these practices.
The data presented here provide:
- An overview of what conservation practices are
being funded,
- Preliminary estimates of unit costs for the most
commonly contracted conservation practices and,
- A comparison of unit costs for different contract
sizes to determine the extent to which economies of
scale exist practice by practice.
All results are presented at the national level, by ERS Farm Resource
Regions, and for ERS Farm Production Regions. A state-by-state breakdown
of the allocation of EQIP funds is also provided.
feature
EQIP: Conserving
While FarmingApplications to participate in the program
have exceeded annual funding, but some participants have opted to
cancel out entirely or withdraw some of the practices specified
in their contracts. This could have implications for program design
and funding, Agricultural Outlook (9/01).
recommended readings
Balancing
Conservation Costs and BenefitsThe growing role of natural
resource conservation in U.S. farm policy is evident in the fivefold
increase in funding for the Environmental Quality Incentives Program
(EQIP) in the 2002 Farm Act. Recognizing the dearth of data concerning
the installation of conservation practices on U.S. farms, ERS has
constructed a database using EQIP conservation practice data. The
database offers a unique opportunity to better understand the demand
for conservation practices across regions, the conservation practices
being funded and implemented, and the unit costs (dollars per acre,
dollars per foot, etc.) of implementing these practices.
media and naming convention
The 10 table files in the EQIP summary database can be downloaded
in either text (Tab delimited) and Excel spreadsheet formats.
File names are listed and described below:
EQIP_FUNDS_NAT Excel spreadsheet Tab-delimited
text file
EQIP_FUNDS_STATE Excel spreadsheet Tab-delimited
text file
EQIP_FUNDS_ERS Excel spreadsheet
Tab-delimited text file
EQIP_FUNDS_FPR Excel spreadsheet
Tab-delimited text file
These files provide data for all EQIP funds allocated during FY1997-FY2000,
by conservation practice, at the national, State, ERS Farm Resource
Region, and Farm Production Region levels.
UNIT_COST_NAT Excel spreadsheet
Tab-delimited text file
UNIT_COST_ERS Excel spreadsheet
Tab-delimited text file
UNIT_COST_FPR Excel spreadsheet
Tab-delimited text file
For some conservation practices (those most commonly implemented
under EQIP), cost data were computed on a per-unit basis. Obtaining
these data required tracking mistaken entries in the database. Given
the database's large size, the unit costs were computed for only
33 conservation practices out of approximately 250 eligible practices.
These files contain the mean unit cost (along with its standard
error) for a practice contracted under EQIP, the median of the unit
cost, and the number of contracted practices used in obtaining the
mean.
SCALE_NAT Excel spreadsheet
Tab-delimited text file
SCALE_ERS Excel spreadsheet
Tab-delimited text file
SCALE_FPR Excel spreadsheet
Tab-delimited text file
The last set of files illustrates, for the 33 conservation practices
for which unit costs were calculated, how the unit cost for a conservation
practice changes as the size of the contract increases. The data
include the median number of units approved for a conservation practice,
and the mean unit cost for the contracts below and those above the
median units approved. Making this distinction highlights whether
larger contracted practices have a lower unit cost due to economies
of scale.
For the files highlighting the economies of scale, only those practices
measured in acres or feet among the 33 selected practices were included.
The excluded practices were all major structural practices (such
as waste storage facilities, wells, ponds, etc.). The excluded practices
are reported in terms of the number of structures involved, which
does not capture the size of the practice. Furthermore, most EQIP
contracts include only one unit of these structural practices leading
to only a few data points to be used for estimating the unit cost
for projects above the usual one unit.
Some of the 33 practices are land management practices, for which
incentive payments are provided, such as:
- Brush management
- Conservation crop rotation
- Irrigation water management
- Nutrient management
- Pest management
- Residue management
- Waste utilization
In all files, the units are provided alongside the variable names
at the top of the column. Where different practices are measured
in different units, no single unit can be defined at the top of
the column. In that case, the physical units (acres, feet, etc.)
used to measure a conservation practice are provided in the column
NRCS_UNIT.
Excel files include a description of the variables as a pop-up
window when the mouse cursor engages the variable name.
data sources and assumptions made in computing the unit costs
All data in the files are derived from Record04 of the FSA EQIP
database detailing approved contracts. The time period covered in
all cases is FY1997-FY2000.
Apparently there were misunderstandings on the convention adopted
for reporting the number of units approved for a conservation practice
in EQIP contracts in this database. The computerized database input
convention requires that the number of units approved be multiplied
by 10 (one implicit decimal place). For example, 10.2 acres should
be entered as 102 in the database. However, in many cases, inordinately
high unit costs are obtained (obtained by dividing the total cost
of completion for a conservation practice by the number of units
approved), arising from the fact that the number of units approved
was not entered with the implicit decimal place. To correct for
this upward bias in the unit costs, a range was established for
the unit cost of each practice. For sample points whose unit cost
was beyond this range, the assumption was made that the units had
been reported without multiplying by 10 and the amount approved
was adjusted accordingly by a factor of 10.
The acceptable
range for unit costs was derived from a sample of State NRCS
field technical guides on the Internet detailing the average costs
of conservation practices. The States used to derive the range were
Alabama, Maine, Missouri, Montana, Ohio, North Dakota, Oklahoma,
Virginia, and Wyoming. The edit criteria adopted were:
Visual inspection of the distribution and the cutoff points indicated
that the method was effective.
For the regionally disaggregated unit-cost files, some of the unit
costs are based on relatively few data points. The standard error
of the mean is a useful indicator of the reliability of the estimate.
The unit costs are calculated by inferring the total cost of the
practice based on the program payment made and what cost-share was
requested. The program allows for 75 percent cost-sharing, but the
maximum rate established by the either the State (for Statewide
resource concerns) or locality (for conservation priority areas)
is often less than the maximum. Also, in the competitive bid process,
some producers will offer to take less than the maximum cost-share
to improve their ranking.
The EQIP program allows incentive payments for a maximum of 3 years,
but requires the practice to be implemented for the term of the
contract. The unit cost presented here may be biased upwards for
these practices.
Land management practices are often cost-effective and producers
will offer to add them to the contract at no cost to improve their
ranking. To avoid biasing the unit cost data, these offers were
excluded from the calculation.
glossary
The National
Handbook of Conservation Practices provides definitions and
information on the EQIP practices. Go to "Alphabetical Listing"
in the document.
updates
This data set will be updated to include FY 2001 data in November
or December 2002.
ERS produces a range of data products available in different formats,
including online databases, spreadsheets, and web files. All data
products online are available at no charge.
|