Wildfire Protection in the
Wildland-Urban Interface
Kelsi Bracmort
Specialist in Agricultural Conservation and Natural Resources Policy
May 15, 2013
Congressional Research Service
7-5700
www.crs.gov
RS21880
CRS Report for Congress
Pr
epared for Members and Committees of Congress

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Wildfire Protection in the Wildland-Urban Interface

Summary
Congressional interest in funding to protect against wildfire threats has focused on communities
in and near forests, an area known as the wildland-urban interface (WUI). The WUI is expanding
in size and population, leading to increased concern for life and property that could potentially be
damaged by wildfires. Approximately 10% of all land in the lower 48 states is classified as WUI.
A significant concentration lies along the East Coast, although western states have the highest
proportions of homes in the WUI.
Federal funding for wildfire protection has increased significantly over the last decade. The U.S.
Forest Service (USFS) and the Department of the Interior (DOI) receive the bulk of funding to
prevent and suppress wildfires. Nearly half of the USFS budget in 2012 was allocated for wildfire
funding. A portion of this funding is spent on WUI efforts.
Wildfire, whether in a WUI community or not, occurs primarily as a surface fire or a crown fire.
A surface fire burns the needles or leaves, grass, and other small biomass within a foot or so of
the ground and quickly moves on. A crown fire burns biomass at all levels, from the surface
through the tops of the trees.
Wildfire suppression involves removing one of the three elements that cause fire—fuel, heat, or
oxygen. A variety of WUI wildfire control efforts may be used for structures, including building
structures to meet protective standards. Some standards vary by state, and many are voluntary,
such as removing burnable materials in proximity of a structure (i.e., defensible space). Control
efforts for protecting wildlands include fuel reduction, or allowing the fire to burn if the
ecosystem is able to adapt to and recover from periodic burning.
Programs and other options exist to address wildfires in the WUI. However, these programs could
be refined to better address the current situation, and new initiatives and funding could be applied
towards WUI issues not yet addressed. For example, programs could be expanded to educate
homeowners, state and local governments, and the insurance industry about the ways to protect
homes through actions, planning, and zoning and building regulations. Congress could consider
expanding protection for defensible space beyond the home ignition zone to a community
protection zone. Congress could also consider appropriating additional funds through the states
for fuel reduction on private lands in the WUI where the treatments would be effective.
Additionally, Congress could consider expanded compensation for landowners who suffer
resource losses from wildfires.
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Wildfire Protection in the Wildland-Urban Interface

Contents
What Is the Wildland-Urban Interface? ........................................................................................... 1
Fire Suppression .............................................................................................................................. 2
In the Aftermath ............................................................................................................................... 4
Minimizing Wildfire Damages ........................................................................................................ 4
Protecting Structures.................................................................................................................. 4
Protecting Wildlands ................................................................................................................. 5
Protecting the WUI .................................................................................................................... 5
Issues for Congress .......................................................................................................................... 6

Figures
Figure 1. 2010 WUI Map ................................................................................................................. 2

Contacts
Author Contact Information............................................................................................................. 8
Acknowledgments ........................................................................................................................... 8

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Wildfire Protection in the Wildland-Urban Interface

ildfires have made national headlines in recent years, with major fires in the West and
South killing firefighters, burning homes, and threatening communities. With the
Wpopulation and size of the wildland-urban interface (WUI) expanding, more money is
being spent on fire management in these locales. Federal funding for fire protection has more than
doubled in the past decade, and administration and congressional leaders have urged additional
wildfire protection. In FY2012, approximately $2.7 billion was spent to protect federal lands and
approximately $104 million to assist in protecting nonfederal lands.1 The U.S. Forest Service
(USFS) in the Department of Agriculture, along with the Department of the Interior (DOI), are
responsible for protecting the majority of federal lands from wildfire, including any federal areas
that comprise a WUI. Wildfire funding accounted for nearly half of the USFS budget and roughly
5% of the DOI budget in 2012. While attention has focused on protecting life, property, and
communities in the WUI, opinions vary over how to provide protection. This report describes the
growth of the wildland-urban interface, wildfire suppression efforts, post-fire responses, and
especially the programs and options for protecting the interface before the next wildfire strikes.
What Is the Wildland-Urban Interface?
The term wildland-urban interface (WUI) has been used for more than two decades to suggest an
area where structures (usually homes) are in or near wildlands (forests or rangelands). There is no
standard WUI definition. However, the definition listed in a 2001 Federal Register notice is
commonly referenced—the urban-wildland interface community exists where humans and their
development meet or intermix with wildland fuel.2 In this same notice, the USFS and DOI
identified three types of WUI communities: interface, intermix, and occluded.3 Based on state
data, they listed nearly 4,500 interface communities (with 11 states not providing data). The
agencies defined an interface community as one where wildlands abut structures with a clear line
of demarcation between residential, business, and public structures and wildland fuels, while an
intermix community is where structures are scattered and intermingled with wildlands and fuels.
An occluded community, generally existing within a city, is where structures abut an island of
wildland fuels (e.g., park or open space).
One source indicates that all states within the contiguous United States contain land classified as
WUI.4 See Figure 1. Furthermore, approximately 10% of all land within the lower 48 states is
classified as WUI, with a significant concentration along the East Coast, although western states
have the highest proportions of their homes in the WUI.5 The area of intermix communities is
large and is growing faster than the area of interface communities, based on data from 1990 to

1 The $2.7 billion spent does not include the additional sum of $407.5 million appropriated in 2013 to repay 2012
wildfire suppression accounts. The amount spent to protect nonfederal lands includes appropriations for the State Fire
Assistance and Volunteer Fire Assistance budget line items from the FS Wildland Fire Management account, $5.0
million for the Biomass Energy Program ($5.0 million annually, FY2009-FY2012), and the State Fire Assistance and
Volunteer Fire Assistance budget line items from the FS State and Private Forestry account. For more information, see
Tables 2 and 4 in CRS Report RL33990, Federal Funding for Wildfire Control and Management.
2 U.S. Dept. of Agriculture and Dept. of the Interior, “Urban Wildland Interface Communities Within the Vicinity of
Federal Lands That Are at High Risk From Wildfire,” 66 Federal Register 753 (January 4, 2001).
3 Ibid.
4 U.S. Forest Service, The Public and Wildland Fire Management: Social Science Findings for Managers, November
2006, http://www.fs.fed.us/nrs/pubs/gtr/gtr_nrs1.pdf.
5 Email from Miranda Mockrin, USFS, May 15, 2013.
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2000.6 In 2010, intermix communities in the three Pacific Coast states totaled 9.3 million acres,
almost three times the 3.6 million acres in interface communities in those states.7 From 1990 to
2000, the 10-year growth in area of intermix communities was 14.1%, compared to only 2.5% for
interface communities. However, the study acknowledged that determining the area of WUI
communities was imprecise: “Mapping [the Federal Register] definition of the WUI using data
and operational definitions we developed, we arrived at one possible representation of the WUI.”8
The intermingled nature of intermix communities poses significant challenges for fire protection
efforts.
Figure 1. 2010 WUI Map

Source: U.S. Forest Service, United States Wildland Urban Interface Maps, 2011, http://silvis.forest.wisc.edu/
maps/wui/state; V. C.Radeloff, R. B. Hammer, S.I. Stewart, J. S. Fried, S. S. Holcomb, and J. F. McKeefry, “The
Wildland Urban Interface in the United States,” Ecological Applications, v. 15 (2005), pp. 799-805.
Fire Suppression
In most of the United States, wildfires are inevitable. Biomass plus dry conditions equals fuel to
burn. Add an ignition source (e.g., lightning or a match) and a wildfire may ignite. Fire is a self-
sustaining chemical reaction that perpetuates itself as long as all three elements of the fire

6 R. B. Hammer, V. C. Radeloff, J. S. Fried, and S. L. Stewart, “Wildland-Urban Interface Housing Growth During the
1990s in California, Oregon, and Washington,” International Journal of Wildland Fire, v. 16 (2007), pp. 255-265.
7 Email from Miranda Mockrin, USFS, May 15, 2013. The data for 2010 is the most recent data available. The FS
states that while WUI data on change from 1990 to 2000 is available, additional data processing is needed before
change information from 2000 to 2010 will be available.
8 Hammer et al., “Wildland-Urban Interface Housing Growth,” p. 256.
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triangle—fuel, heat, and oxygen—remain available. Fire control focuses on removing one of
those elements.
There are two principal kinds of wildfire, although an individual wildfire may contain areas of
both kinds.9 A surface fire burns the needles or leaves, grass, and other small biomass within a
foot or so of the ground and quickly moves on. Such fires are relatively easy to control by
removing fuel with a fireline, essentially a dirt path wide enough to eliminate the continuous fuels
needed to sustain the fire, or by cooling or smothering the flames with water or dirt.10
A crown fire burns biomass at all levels, from the surface through the tops of the trees. Crown
fires do not consume all the biomass; rather, a crown fire quickly burns the needles or leaves and
small twigs and limbs on the surface and throughout the crown of the trees. Because the needles
and leaves in the crown are green, they require more energy to burn than dry fuels on the surface.
Furthermore, because of the green fuels and the often discontinuous biomass of the canopy, wind
is usually needed to sustain a crown fire. Once burning vigorously, a crown fire can create its own
wind—the strong upward convection of the heated air can draw in cooler air from surrounding
areas, thus creating a wind that feeds the fire. The strong upward convection can also lift burning
biomass (firebrands) and send it soaring ahead of the fire, creating spot fires and accelerating the
spread of the wildfire. Thus, crown fires are difficult, if not impossible, to control. Firelines are
often ineffective, especially if winds are causing spot fires. Water or fire retardant (slurry)
dropped from helicopters or airplanes can sometimes knock a crown fire down (back to a surface
fire) if the area burning and the winds are not too great. Often, however, crown fires burn until
they run out of fuel or the weather changes (the wind dies or it rains or snows).
Fires burn structures in one of three ways: through direct contact with fire (the fire burning right
up to the structure); through radiation (heating from exposure to flames); and through firebrands
landing on a flammable roof.11 Surface fires generally only burn houses through direct contact,
and protection is a relatively simple matter of a break in the continuous burnable material. In
observing houses that burned in Los Alamos in 2000, one researcher stated “in several cases, a
scratch line that removed [pine] needles from the base of a wood wall kept the house from
igniting.”12 Crown fires, however, can burn houses in any of the three ways. The opportunity and
ability to prevent structures from burning during a crown fire is small. Occasionally, water or
some other wetting agent sprayed on walls or roofs can prevent ignition or extinguish firebrands
from an advancing wildfire, but the firefighters could die of heat exposure or smoke inhalation
from the approaching fire.

9 See S. F. Arno and S. Allison-Bunnell, Flames in Our Forest: Disaster or Renewal? (Washington, DC: Island Press,
2002), pp. 45-46.
10 A fireline may be as narrow as 1 foot for suppressing a fire in shortgrasses and light fuels, or can be more than 100
feet wide for heavier-fueled fires. U.S. Forest Service, About Handcrews, http://www.fs.fed.us/fire/people/handcrews/
about_handcrews.html.
11 National Wildland/Urban Interface, Fire Protection Program, Wildland/Urban Interface Fire Hazard Assessment
Methodology, p. 5, at http://www.firewise.org/resources/files/wham.pdf.
12 Jack Cohen, “The Cerro Grande Fire: Why Houses Burned,” Forest Trust Quarterly Report, no. 13 (December
2000): p. 11.
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In the Aftermath
Recovery and efforts to support recovery after a severe wildfire vary, depending on the nature of
the damages. For burned structures, insurance payment is the standard means for homeowners to
pay for recovery—repair, if that is possible, or replacement, depending on the insurance policy. In
a severe event, a presidential declaration of an emergency (in response to a request from a
governor) initiates a process for federal assistance to state and local governments and to families
and individuals to help with recovery. The nature and extent of the assistance depends on several
factors, such as the nature and severity of damages and the insurance coverage of the affected
parties.13
For burned areas, site rehabilitation is sometimes warranted. In many temperate ecosystems,
wildfires (including crown fires) are natural events, and the ecosystems are adapted to recover
from the fire. Often, in severely burned areas, grass seed is spread to try to accelerate growth of
ground cover and slow erosion, but grass often inhibits tree seed germination and growth, and
thus may slow forest recovery. Rehabilitation efforts commonly focus on the firelines created to
try to control the fire, since firelines consist of exposed bare earth and often run uphill, and thus
can readily erode into gullies if left untreated. Some severely burned areas, particularly in coastal
southern California, are susceptible to landslides during the subsequent rainy season. Monitoring
can provide a warning to homeowners to evacuate an area prior to a landslide, but little can be
done to prevent landslides in such situations.
Minimizing Wildfire Damages
Various efforts can protect structures and wildlands from some of the damages of wildfires.14
Protecting Structures
A structure’s characteristics and landscaping significantly affect its chance of surviving a wildfire.
Evidence from models, experiments, and case studies demonstrates that structural characteristics,
especially the roofing materials, largely determine whether a home burns in a wildfire. Homes of
brick or adobe with non-flammable roofs (e.g., tile, slate, metal) are far less likely to burn than
homes with wood siding and flammable roofs (e.g., wood shingles).15 Burnable materials (such as
trees, shrubs, grass, pine needles, woodpiles, wood decks, and wooden deck furniture) within 40
meters (131 feet) of the structure also strongly influence whether the structure burns in a
wildfire.16

13 For more information, see CRS Report RL34146, FEMA’s Disaster Declaration Process: A Primer, by Francis X.
McCarthy; and CRS Report RL33053, Federal Stafford Act Disaster Assistance: Presidential Declarations, Eligible
Activities, and Funding, by Francis X. McCarthy.
14 See CRS Report RL34517, Wildfire Damages to Homes and Resources: Understanding Causes and Reducing
Losses.
15 Jack D. Cohen, “Preventing Disaster: Home Ignitability in the Wildland-Urban Interface,” Journal of Forestry, v. 98,
no. 3 (March 2000): 15-21.
16 Cohen, “Preventing Disaster.”
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Furthermore, the structure and landscape characteristics are more important than the intensity of
the fire in determining whether a house burns. The Hayman Fire, in Colorado in June 2002,
burned 132 houses—70 houses (53%) were surrounded by crown fire, while 62 houses (47%)
were surrounded by surface fire.17 In addition, 662 homes (83% of all homes within the fire
perimeter) survived the fire, even though 35% of the area was severely burned and 16% was
moderately burned.18 This suggests that at least some of the structures survived despite a crown
fire around them.
Protecting Wildlands
The impact of wildfires on wildlands depends largely on the nature of the ecosystem. Some
ecosystems are adapted to and recover from periodic crown fires—perennial grasslands,
chaparral, lodgepole and jack pines, and more. In these ecosystems, the plants have evolved to
resprout or reseed the burned areas, and thus recover from crown fires by outcompeting other
plant species. Eliminating crown fires could eventually eliminate these ecosystems. However,
eliminating crown fires in these ecosystems is probably impossible, since the plants contribute to
the development and spread of crown fires—grasses burn quickly; chaparral has a high volatile-
oils content; and lodgepole and jack pines grow in dense, even-aged stands.
Other ecosystems are adapted to relatively frequent (5- to 35-year intervals) surface fires. Fire
suppression has been moderately successful in controlling surface fires, and thus the needles,
twigs, and other fine and small fuels have been accumulating for three or more fire cycles. This
abnormal fuel accumulation, combined with fuel ladders of brush, small trees, and low limbs
(many of which would have burned in a surface fire), have led to crown fires where such fires
were historically rare. Fuel reduction treatments can restore conditions in frequent-surface-fire
ecosystems to again make crown fires rare occurrences, reducing damages to resources.
Protecting the WUI
Reducing fuels in the WUI has been a controversial aspect of congressional debates over fire
protection legislation. The evidence discussed above indicates that fuel reduction provides little
protection for structures. However, some observers have noted that the WUI is more than just a
collection of houses:19
A town is not just the place where people have homes. Communities are in the forest because
they are emotionally, economically, and socially linked and dependent on the forest. When we
consider the areas that need immediate treatment we should consider the human community
“impact area”—the entire area that, if impacted by a catastrophic fire, will undermine the health
and livelihood of a community.

17 Jack Cohen and Rick Stratton, “Home Destruction Within the Hayman Fire Perimeter,” Hayman Fire Case Study,
Gen. Tech. Rept. RMRS-GTR-114 (Ft. Collins, CO: USDA Forest Service, September 2003), p. 264.
18 Peter Robichaud, Lee MacDonald, Jeff Freeouf, Dan Neary, Deborah Martin, and Louise Ashman, “Postfire
Rehabilitation of the Hayman Fire,” Hayman Fire Case Study, Gen. Tech. Rept. RMRS-GTR-114 (Ft. Collins, CO:
USDA Forest Service, September 2003), p. 294.
19 W. Wallace Covington, Director, The Ecological Restoration Institute, Northern Arizona University, “Prepared
Statement,” National Fire Plan, hearing before the Senate Committee on Energy and Natural Resources, July 16, 2002,
S.Hrg. 107-834 (Washington, DC: GPO, 2003), p. 61.
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At a minimum, most would agree on the need for an area of defensible space around homes that
needs to be cleared of burnable materials—at least 10 meters (33 feet) and possibly as much as 40
meters (131 feet). One observer recommended that protecting communities should include
intensive treatment to reduce fuels and burnable materials in the home ignition zone, up to 200
meters (655 feet) around structures, with less intensive fuel treatment in the community protection
zone, generally up to 500 meters (1,640 feet, or about a third of a mile) from structures.20
The National Fire Protection Association’s (NFPA’s) Firewise Communities program assists
communities with specific wildfire safety needs. The term “Firewise” describes the goal of
teaching residents about wildfire and about smart practices around their homes that can reduce the
risk of destruction. The program started in 1986 as a national project and gradually evolved to
become a national program in 2002. The program, co-sponsored by the USFS, DOI, and the
National Association of State Foresters, encourages local solutions for wildfire safety by
involving homeowners, community leaders, planners, developers, firefighters, and others in the
effort to protect people and property from wildfire risks.
The Healthy Forests Restoration Act of 2003 (HFRA; P.L. 108-148; 16 U.S.C. §6511) established
a somewhat broader standard for fuel reduction activities under its authorities. Section 101(16) of
HFRA defined the WUI to include an area out to ½ mile from the boundary of an at-risk
community or 1½ miles from the boundary if a sustained steep slope could cause dangerous fire
behavior or to an effective fire break, such as a road or ridge top. HFRA included no guidance on
how to apply these standards in intermix communities, with no definitive boundary.
Issues for Congress
While there have been slightly fewer total fires in recent years as compared to a peak experienced
in 2006 and 2007, more than 9.3 million acres burned in 2012, which was the third-largest
acreage burned annually since 1960.21 Thus, people are still at risk from wildfires when they
occur in the WUI. The National Interagency Fire Center (NIFC) reports that 4,244 structures
burned in 2012.22 Congress faces increasing pressures for wildfire protection. Congress decides
what programs to authorize and fund to protect the WUI from wildfires. Many programs exist,
and other options are possible.
Since FY2008, suppression has usually received the majority of wildfire management funding,
ranging from $800.0 million to $1.4 billion annually (not including emergency supplemental
funds) since FY2008.23 Appropriations for wildfire suppression have risen in nearly every year
for a decade, going from $277 million for FY1999 to $808.4 million for FY2012 (not including
emergency supplemental funds). The public and policymakers expect the agencies to clearly
demonstrate that they are doing what they can to stop threatening and damaging fires, and this
often involves large sums of money. However, given the difficulty of suppressing crown fires, and

20 Brian Nowicki, Effectively Treating the Wildland-Urban Interface to Protect Houses and Communities from the
Threat of Forest Fire (Tucson, AZ: Center for Biological Diversity, August 2002).
21 National Interagency Fire Center, Wildland Fires and Acres.
22 Structures include primary residences, commercial buildings, outbuildings and seasonal dwellings. Information
provided in an email from NIFC on May 7, 2013.
23 There was a budget restructure in FY2012 which now directs more money to preparedness.
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the difficulty and cost associated with measuring what has burned and what was suppressed,
some may question the effectiveness of continued increases in suppression funding.
To date, Congress has mostly addressed wildfire prevention and suppression by increasing
funding. It is difficult to gauge if the funding amounts provided by Congress each year are
adequate. National data on what transpired during the year are hard to locate and are disjointed
when available. More comprehensive and accurate national performance measures (e.g., number
of fires that started on federal lands, number of structures burned due to wildfires) could give
better insight into the effectiveness of wildfire prevention and suppression efforts.24 National
wildland fire data collection and analysis could start with Congress explicitly requesting the
numerous fire reporting agencies to work together to provide annual statistics and performance
measures.25 Such a directive could require more resources than are available at the moment.
Given the current economic climate, better national data could provide insight as to whether or
not other options to address wildfire management (e.g., a reduction in funding or a do-nothing
approach) should receive more careful consideration.
Federal programs to protect homes are currently limited to information for homeowners on how
to protect their homes, primarily provided through the NFPA Firewise Communities program.
Programs could be expanded to educate homeowners, state and local governments, and the
insurance industry about the ways to protect homes through actions, planning, and zoning and
building regulations. Congress could create and fund new programs to assist homeowners in
renovations to make their homes fire-safe and to create defensible space around their structures,
through direct federal assistance or through the states.
Congress could also consider expanding protection for defensible space beyond the home ignition
zone to a community protection zone. HFRA authorizes an expedited review process for activities
on federal lands in the WUI. Perhaps other changes could further accelerate action. Funding for
fuel reduction in the WUI could also be expanded. Appropriations for fuel reduction have
averaged $516.0 million annually since FY2008, but only a portion is used in the WUI, and
funding is far below the estimated amount needed to treat the lands at risk.26 State fire assistance
funding through the Forest Service could be used for fuel reduction in the WUI, at the discretion
of the states, but funding has averaged $163 million annually from FY2008 to FY2012 and the
states have many wildfire priorities.27 Additional funding through the states for fuel reduction on
private lands in the WUI is a possibility that Congress could contemplate.
In addition, Congress might debate choices for compensating homeowners for property losses due
to wildfires. One option might be to restrict compensation to those who had acted to protect their

24 This is not a new issue. The Government Accountability Office (GAO) has produced numerous reports addressing
various aspects of fire strategies by both the FS and DOI. The most recent GAO report discusses measures federal
agencies can take to ensure that federal dollars, on a national basis, are spent wisely on wildland fire prevention. U.S.
Government Accountability Office, Federal Agencies Have Taken Important Steps Forward, but Additional, Strategic
Action Is Needed to Capitalize on Those Steps, GAO-09-877, September 9, 2009, http://www.gao.gov/products/GAO-
09-877.
25 Most wildland fire data comes from NIFC, USFS, and NFPA.
26 See the discussion in CRS Report RL33990, Federal Funding for Wildfire Control and Management.
27 The average is based on state fire assistance funding appropriated under the wildland fire management (WFM)
account and the state and private forestry (S&PF) account for FY2008-FY2012. The WFM account state fire assistance
funding average is $129 million, and ranged from $250 million in FY2009 to $55.5 million in FY2012. The S&PF
account state fire assistance funding average is $33.9 million.
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homes, but got burned anyway. Another option might be to require that compensation for
rebuilding be used only for fire-safe building designs and materials. Alternatively, Congress could
establish a national wildfire insurance program, with premiums based on fire threats, the fire-
safety of the structures, and the defensible space being maintained.
Finally, Congress could consider compensation for landowners that suffer resource losses from
wildfires. An emergency reforestation assistance program has existed for many years, although it
has not been funded since FY1993.28 In the 2008 farm bill, Congress included forest restoration
assistance in an existing emergency conservation program.29 These programs can provide
assistance in recovery from a wildfire disaster, but do not compensate landowners for losses in
the way that homeowners are compensated for the loss of their homes. Congress might consider
such additional compensation.
The 113th Congress has proposed legislation that would address some of the issues stated above.
For example, H.R. 818 could expand authorities established under the Healthy Forest Restoration
Act of 2003 (P.L. 108-148) that could allow states a more pronounced role in designating high-
risk areas for emergency hazardous fuel reduction projects, among other things. Also, H.R. 1345
could expedite the implementation process for eligible wildfire prevention projects, among other
things. In the 112th Congress, H.R. 1485 would have, in part, authorized an expedited review
process by the FS and DOI for fuel reduction and forest restoration projects in the WUI. And in
the 112th Congress, some measures were introduced that would have reduced wildfire program
funding, such as H.Amdt. 764 to H.R. 2584, which sought to reduce funding for the Wildfire
Suppression Program by $50 million and to increase funding for the Forest Legacy Program by a
similar amount.

Author Contact Information

Kelsi Bracmort

Specialist in Agricultural Conservation and Natural
Resources Policy
kbracmort@crs.loc.gov, 7-7283


Acknowledgments
This report was originally written by Ross Gorte, retired CRS Specialist in Natural Resources Policy. The
listed contact has updated the original report and is available to respond to inquiries on the subject.


28 See CRS Report RL31065, Forestry Assistance Programs.
29 See CRS Report RL33917, Forestry in the 2008 Farm Bill.
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