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Record closed August 20, 2026
High threat to public lands

Stop commercial logging on Cherokee National Forest

Sugar Mountain

U.S. Forest Service· Sugar Mountain, Cherokee National ForestU.S. Forest Service project page ↗

Forest ServiceWe track this on the agency’s own system of record, where most on-the-ground decisions live.

Wild turkey in hardwood forest
Pictured: Wild turkey in hardwood forest

The groups on this fight

4 groups work Tennessee

By footprint, from the same match the STAND matchmaker runs; none is linked to this decision in our record yet. Give straight to them; nothing routes through us.

Every group above is on STAND for Public Lands, with its court record, its filings and who backs it.

The Forest Service plans to cut timber on Sugar Mountain and reshape its forests for decades.

What’s at risk

Mature forest on Sugar Mountain in Cherokee National Forest faces commercial logging and habitat conversion under this proposal. The agency would permanently alter tree cover and wildlife habitat through timber harvest and related ground disturbance.

If this goes through

Commercial logging and forest clearing will reshape Sugar Mountain's landscape, with effects on mature trees and native habitat that cannot be quickly undone.

Our plain-English read of the official notice ↗. Check it against the agency’s own words below.

10 holes in the agency’s own analysis

What the public could have raised, from the agency’s own document

  • I oppose this action as proposed, and I ask the agency to weigh the specific harms below.
  • The EA's own Biological Assessment summary discloses a 'May Affect, Likely to Adversely Affect' determination for the Indiana bat, with approximately 3,537 acres of preferred summer roosting habitat impacted, yet the agency dismisses further site-specific analysis by simply tiering to a prior Programmatic Biological Opinion without showing that this project's specific footprint, acreage, and timing were actually evaluated in that consultation. Given this is the most serious effects finding in the whole document for any listed species, the agency should directly analyze in the EA (not just by reference) how this project's impacts were quantified within the Programmatic BO's scope, or prepare a project-specific Biological Opinion and an EIS given the likely adverse effect finding.
  • Section 3.3.5 directly contradicts itself on prescribed fire in the Queen Cove/North River bog rare community. The affected environment discussion states that approximately 98 acres of this rare, fire-intolerant wetland bog complex are proposed for burning as part of the Whigg Ridge burn unit, but the mitigation measures in the same section state that no ignition of prescribed fire is permitted within that same rare community. The agency needs to reconcile this contradiction, clarify the actual burn unit boundary relative to the rare community boundary, and disclose whether the 98 acres figure is accurate or an error, before the public can meaningfully comment on impacts to this unique, non-fire-adapted plant community.
  • The document's own fire-effects analysis, drawing on Pistrang's white paper, concludes that rich cove, acid cove, and northern hardwood forest communities are fire-sensitive and states plainly that prescribed fire is not an appropriate tool there, ending with an explicit recommendation against burning. Yet Table 6 shows these same ecozones (Acidic Cove Forest, Rich Cove Forest, Northern Hardwood Slope Forest, Northern Hardwood Cove Forest) occupy thousands of acres within the project boundary and some fall within harvest unit and fire return interval acreage. The agency should explain how burn unit boundaries were drawn to exclude these community types or revise the proposed action to remove them from prescribed fire treatment as its own specialist recommended.
  • Section 3.4.1 asserts that water quality in project-area streams is good and that all streams are fully supporting designated beneficial uses, while in the same breath acknowledging ongoing sediment delivery and altered stream morphology from roads near the Tellico River, North River, and their tributaries. The agency treats this acknowledged degradation as consistent with 'good' water quality without reconciling the two statements or explaining the threshold at which sediment and morphology changes would become a beneficial-use impairment. The agency should directly analyze the cumulative sediment and morphology impacts already occurring from roads before concluding new ground-disturbing activities pose only low risk.
Show all 12 points from the document
  • The entire watershed impervious-surface and sediment-risk analysis in Section 3.4 relies on National Hydrography Dataset stream data that the agency's own hydrologist and botanist found to be incomplete during 2025 field reviews, having observed multiple intermittent and ephemeral streams not captured in that dataset. Because drainage density directly drives the Total Impervious Area calculations used to conclude the project will stay below the 10% TIA significance threshold, an underestimated stream network could mean the actual TIA and connected sediment risk are higher than disclosed. The agency should recalculate TIA and buffer requirements using the field-verified stream locations before relying on the 10% threshold conclusion.
  • The purpose and need section sets RLRMP Objective 12.01 as a goal of maintaining at least 1,000 acres above 3,000 feet in grassy/herbaceous habitat, but the proposed action would only increase permanent high-elevation early successional habitat from 23 to 38 acres. The agency frames this 15-acre increase as a '65% increase towards RLRMP objectives,' a percentage calculated relative to the tiny existing baseline rather than relative to the 1,000-acre objective, which this project would move only a few percent toward. The agency should disclose the percentage of the 1,000-acre objective actually achieved by this project and explain why such a small contribution justifies the scale of proposed harvest and burning.
  • In responding to scoping comments, the agency insists that timber volume was 'never considered' as a project need, yet its own listed rationale for using commercial harvest over non-commercial alternatives explicitly includes that it 'generates income to be used in stewardship projects on the forest' and 'supports the local economy.' These are volume- and revenue-related justifications, which undercuts the agency's categorical claim that volume was not a driver of alternative selection. The agency should clarify whether revenue generation was in fact a factor in choosing commercial harvest over smaller-scale non-commercial methods, and reconsider alternatives that were rejected partly on cost/volume grounds.
  • The water and soil effects analyses repeatedly acknowledge that the modeled sequence of activities is unrealistic and that the disclosed effects 'may be an overestimate of those that will actually occur' because real implementation is spread out and less concentrated in time than assumed. While this framing is used to support a low-risk conclusion, the agency never runs or discloses a lower-bound or most-likely scenario, only the admittedly inflated one, making it impossible for the public to assess whether the 'low risk' conclusion would hold under more realistic assumptions of overlapping activities. The agency should disclose a realistic-case sediment and soil disturbance scenario alongside the conservative one.
  • The Detrimental Soil Disturbance analysis in Section 3.5.2 relies on a preliminary logging plan and multiple stacked assumptions (assumed road width of 21 feet, assumed landing size of 0.25 acres, assumed harvest system) to conclude that no unit exceeds the 15% DSD significance threshold, but Table 11 shows several units projected at 10-12% cumulative DSD, leaving little margin, and the text itself states these DSD 'values are not absolute' and depend on final harvest system, unit boundaries, and operator skill that are not yet determined. The agency should finalize the logging plan and unit layout before concluding no significance threshold will be exceeded, or disclose a margin-of-error range for the DSD estimates.
  • The stated need to create ruffed grouse habitat rests heavily on drumming surveys conducted on only three roads over three years, averaging just one detection per year across the entire district, a very thin data set used to justify a multi-hundred-acre vegetation management program. The agency should disclose the statistical confidence and limitations of this small sample size and supplement it with additional monitoring or peer-reviewed regional trend data before relying on it as the primary justification for the scale of the proposed harvest and burning program.
  • Say something only you can say. The law requires the agency to consider and respond to substantive comments, and specifics are what make a comment substantive.
Every point is checked against the agency’s own decision document ↗. 10 findings verified against the text, word for word.

In the agency’s own words

The Sugar Mountain Project would utilize commercial timber harvest, wildlife opening enhancements, timber stand improvements, prescribed fire, and other associated actions to increase early successional habitat and improve forest health.

U.S. Forest Service project page ↗

The reporting behind this

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