Burning the myth: Why western forests need management grounded in reality

The national forests of western Montana, Idaho and Washington are not abstract landscapes. They are lived-in, worked-in, fire-prone places shaped by more than a century of decisions, constraints, and unintended consequences. 

Boundary County sits at the center of this story. Our forests have burned, regrown, been restricted, litigated, locked up, and — when we were allowed — successfully restored. If we are going to talk honestly about the future of western forests, we must begin by grounding the conversation in what history actually shows.

The first reality is that these forests have never been static. The Big Burn of 1910 reset the entire Panhandle, replacing old-growth cedar and white pine with dense lodgepole pine that grew thick, uniform, and primed for fire. By the 1960s, that lodgepole belt stretched from Shoshone County to the Canadian border — an over‑mature, tightly packed fuel source waiting for a spark. In 1967, it got two: the Sundance Fire and the Trapper Peak Fire. Together they burned more than 70,000 acres in a matter of days, long before modern climate change became a factor. Their severity was driven not by temperature but by fuel.

That pattern has repeated itself for more than a century. Catastrophic fires have occurred in cool decades, warm decades, wet decades, and dry decades — but always in forests overloaded with fuel. Climate change now lengthens fire seasons and increases the number of high‑risk days, but it does not create fuel. Policy does. Decades of fire suppression, the 1975 grizzly listing, the 1984 caribou listing, and the 2001 Roadless Rule collectively restricted thinning, road access, and timber harvest across millions of acres. The result was predictable: timber harvests in the Idaho Panhandle and Kootenai National Forests collapsed by more than 90 percent from their early‑1980s levels. But the forests didn’t stop growing. They grew faster than ever.

This is the second reality: timber is a renewable resource, and the United States has never harvested more than grows back. Even at peak harvest — 400 to 500 million board feet per year in the 1970s and early 1980s — annual forest growth exceeded removals. The forest base expanded. Fuel loads stayed in balance. When harvests collapsed, the imbalance began. Today, unmanaged stands contain three to ten times the fuel loads of their historical conditions.

The third reality is that non‑management is not neutral. Leaving overstocked forests untreated does not preserve them — it subjects them to unplanned transformation through severe wildfire, insect outbreaks and watershed degradation. Boundary County has lived this firsthand. When the Myrtle Creek watershed burned, the city of Bonners Ferry, the Forest Service, and local partners launched a Herculean restoration effort: stabilizing slopes, reseeding, replanting, repairing culverts and reinforcing streambanks. The watershed recovered because people acted. Myrtle Creek is proof that when local communities are allowed to manage their forests and watersheds, they do it well.

Yet the gap between ecological need and management capacity continues to widen. Land managers face staffing shortages, contracting limitations, litigation risk and administrative processes that delay even widely supported projects. These systems exist for good reasons — public accountability, environmental protection and stakeholder involvement — but they are not functioning at the pace the landscape requires. Reform is needed not to eliminate oversight but to ensure that oversight does not substitute for action.

Mechanical thinning, prescribed fire, and strategically designed timber harvest remain the only scalable tools capable of reducing fuel loads across broad landscapes. Their effectiveness depends on thoughtful design, long‑term maintenance, and cross‑boundary coordination. They also depend on the infrastructure — mills, contractors, equipment and workforce — that decades of declining harvests have eroded. In the Inland Northwest, the debate over timber harvest cannot be reduced to caricatures of “logging versus conservation.” It must be grounded in site‑specific analysis, ecological evidence, and the recognition that unmanaged forests carry their own ecological and social costs.

Western national forests are not museum pieces insulated from human influence. They are dynamic systems already shaped by roads, past harvest, grazing, recreation, fire suppression and now climate change. Delaying decisions does not prevent change — it simply shifts it into the realm of crisis response. The question is not whether we will manage these forests, but whether we will do so deliberately or by default through megafire.

A realistic path forward requires sustained funding for hazardous‑fuel reduction, expanded workforce capacity, streamlined but accountable environmental review, stronger tribal and community engagement and adaptive management frameworks that evolve with new science. It requires acknowledging that uncertainty is not an excuse for inaction. And it requires moving beyond the false choice between “pristine nature” and unrestricted intervention.

The lesson from Boundary County’s history is clear:

When we manage forests, they remain resilient.

When we don’t, they burn.

The future of western forests depends on whether we are willing to act on that reality.

DARRELL KERBY

Bonners Ferry