
Douglas MacCleery, Assistant Director of Timber Management, USFS, National Forest Mission Shift: How to Respond to Changing
Public Preferences, March 1998:
“Over the last two decades, public debate over how National Forest System lands should be used and managed has become ever more intense and polarized, reflecting a lack of public agreement on the overall mission that should govern these lands. This lack of agreement, coupled with implementation of federal environmental laws, has had the effect of substantially reducing commodity outputs from National Forest lands, increasing emphasis on amenity values, and on maintaining and restoring ecosystem function, biological diversity and health.”
![]() Turn-of-the-century cabin— This Forest Service photograph is thought to be of one of the first Ranger cabins constructed in Montana. Back then, District Rangers traveled their vast territories on horseback, and often fought forest fires with nothing more than shovels and axes. The children are unidentified but are probably the Ranger’s. |
These changes—political and scientific—transect five distinct eras in the history of the National Forest System: 1905–1950, the 50s and 60s, the early 1970s, the mid-70 to mid-80 period and the mid-80s forward.
The 1905–1950 period is often called “the custodial era.” Little harvesting occurred and few people ventured into National Forests. Between 1896, when Congress created the first Forest Reserves, and 1910, the emerging National Forest System grew from 18 to 168 million acres. The System was created for two reasons: to protect watersheds and to serve as a future source of timber for a fast growing nation. But until the post-World War II era there was little demand for National Forest timber. Controlling wildfires— prerequisite to long-term management —was a priority, and livestock grazing was the primary commercial activity. During the Depression years, the Civilian Conservation Corps (1933–1942) built most the trails and campgrounds found in National Forests today. CCC boys also fought fires and thinned forests, but most notably they planted 1.365 billion trees.
Things changed quickly following the end of World War II. GI’s returning from the war got married, started families and bought homes. Demand for timber soared and with it the National Forest harvest level. From the late 1940s to the mid-1960s, the annual harvest level rose from 2.0 to 14 billion board feet, a harvest sufficient to meet 20 percent of total U.S. wood consumption.
During this same period, an increasingly mobile and affluent population began putting a new kind of pressure on National Forests. Demand for recreation soared, rising from 18 million visitor days in 1946 to 233 million in 1975.
In 1960, Congress passed the Multiple Use-Sustained Yield Act mandating that National Forests be managed for multiple values: recreation, wildlife, timber, grazing and watershed protection. The act was the first of several new laws reflecting increased social unrest and growing public concern for the environmental impacts of timber harvesting. Others passed between 1960 and 1976 included the Wilderness Act, 1964; the National Environmental Policy Act and the Clean Air Act, 1970; the Clean Water Act, 1972; the Endangered Species Act, 1973; the Forest and Range Lands Renewable Resources Planning Act, 1974; and the National Forest Management Act, 1976. Despite these protections the increasingly rancorous National Forest debate has come to focus solely on whether any harvesting should be permitted in these forests, no matter the reason.
Between 1987 and 1995, National Forest harvest levels in Oregon, Washington and California—the epicenter of the spotted owl-old growth debate— dropped 89 percent, from 6.86 to 0.78 billion board feet annually. Elsewhere in the National Forest System, the harvest level dropped 53 percent, from 4.46 to 2.10 billion board feet a year. Even more revealing is the kind of harvesting that is occurring.
![]() Harvest decline—Since 1993, National Forest commodity harvesting—harvesting in response to consumer demand has declined from 71 to 52 percent of total harvest volume. Meanwhile, “stewardship harvesting”—harvesting to improve forest health, create wildlife habitat or reduce the risk of catastrophic fire—has increased from 24 to 40 percent of total harvest. ( Changing Economics of National Forest Timber Sale Program, USFS, 1999) |
Today, 42.8 million acres—23 percent of the 191 million-acre National Forest System—is statutorily set aside in noharvest areas. These include the National Wilderness Preservation System, 34.6 million acres; National Monuments, 3.4 million acres; National Recreation Areas, 2.7 million acres; National Game Refuges and Wildlife Preserves, 1.2 million acres; Wild and Scenic Rivers and Scenic and Primitive areas, .9 million acres.
Where harvesting is still permitted, the shift toward selective removal of dead and dying trees underscores both a recognition of changing public values and a steady ecological decline in the West’s National Forests. In the Interior West, more than twice as much timber dies annually than is harvested: 2.0 billion board feet died in 1997 and 744 million board feet were harvested. This is the “forest health problem”expressed in numbers —and what the numbers reveal is that wide areas within the western National Forest System are no longer able to function naturally— meaning the presence of natural agents such as insects and diseases often lead to catastrophic consequences, usually fire. But because restoring forest health is often linked to a need to thin dense stands, many environmentalists view it as little more than an excuse to harvest timber. Skepticism notwithstanding, the increasing frequency of increasingly destructive forest fires suggests many of the West’s National Forests are unhealthy.
Big fires tell only the most visible part of the forest health story. Less visible but ultimately more dangerous is the startling increase in the number of small trees. The volume of trees less than 17 inches in diameter has increased 52 percent since 1952—in part because replanted forests were rarely thinned before they became commercially viable. Moreover, the public’s aversion to fire made controlled burning politically undesirable, even in fire-dependent ecosystems where it would have helped control insects, diseases and stand density.
System-wide, National Forest net annual growth (gross tree growth minus mortality) has been increasing steadily since the 1950s and is nearing 16 billion board feet per year. Meanwhile, annual harvest hovers between three and four billion feet, meaning that growth exceeds harvest by about 400 percent. Most forest scientists agree that such outsized net growth is not sustainable. The Forest Service estimates that between 39 and 43 million National Forest acres could benefit from a long-term thinning program designed to reduce the risk of catastrophic fire, but if Congress approves the proposed harvest ban such thinning would be illegal.
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National Forest System Growth and Removals: 1952-1991—Since the early 1950s, net annual forest growth in National Forests has exceeded harvesting by a wide margin. Meanwhile, average forest biomass per acre has increased steadily—in 1994 by 2.8 billion cubic feet, almost 3 times harvest volume. Shown here, a second growth Douglas-fir stand on Oregon’s Umpqua National Forest. (USFS cut and sold reports) |
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National Forest Net Growth and Removals, Interior West: 1952–1991—Green biomass accumulations are greatest in Intermountain National Forests, a result of the exclusion of fire from fire-dependent ecosystems. Since 1952, the volume of trees less than 17 inches in diameter has increased 52 percent. Today, such trees account for two-thirds of total stand volume in the Interior West. As biomass increases, so too do the risks posed by insects, diseases and wildfires. Shown here, dense— and dying—stand on Idaho’ s Nez Perce National Forest. (Forest Resources of the U.S., USFS, 1992) |
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Trends in Forest Structure, Flathead National Forest: 1899–1991—The absence of fire is not just causing forests to become more dense; many forests are also older on average than they would have been had fire been more prevalent in this century. In 1899, 18 percent of western Montana’s Flathead National Forest was mature and 6 percent was old growth; but by 1990, 33 percent of the forest was mature and 20 percent had achieved old growth status. Just how long this publicly desired condition can be retained in the face of increasing disease and fire is an unanswerable question. (USFS, Flathead National Forest) |
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Trends in National Forest Harvesting: Sawtimber versus Non-Sawtimber—Since 1989, the volume of “sawtimber”— softwood trees at least 9 inches in diameter breast high—has declined from about 12 billion board feet annually to less than 4 billion board feet. Meanwhile, nonsawtimber volume—trees less than 9 inches in diameter—has increased from 20 to 40 percent of total annual harvest. Shown here, big logs moving off Oregon’s Rogue River National Forest in 1990. (USFS) |
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Trends in National Forest Harvesting: Green versus Salvage Volume— Historically, most of the trees harvested from National Forests were live or “green,” but now “salvage” harvesting—the removal of diseased, dying or dead trees that pose a fire hazard—accounts for 40 percent of National Forest harvesting. The shift from “green” to “salvage” volume is consistent with the shift from “commodity” harvesting to “forest stewardship” management practices designed to improve habitat, reduce the risk of fire or conserve biological diversity. Shown here, delimber works on small logs harvested from a 1996 thinning in Montana’s Lolo National Forest in 1996. (USFS) |
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Trends in National Forest Harvesting: the Decline in Clearcutting—Since 1989, the number of National Forest acres harvested annually has declined by 55 percent and, since 1992, the acres that are clearcut annually has declined 72 percent. Today, less than one percent of all National Forest acres classified suitable for harvesting are harvested annually. Shown here, a mid-1980s clearcut on Oregon’s Siskiyou National Forest. (USFS) |