Ecosystem Integrity

Intact roadless landscapes support functional soils, hydrology, and food webs that fragmented forests cannot replicate.

Overview

Intact forests do work. They filter water through layers of duff and root structure, releasing it to streams cold, clear, and slowly. They cool the ground beneath them and the air above. They store carbon in living trees, fallen logs, and the deep organic soils that take centuries to develop. They support food webs that depend on the relationships between predators and prey, fungi and roots, pollinators and plants — relationships that exist only when all the components are present. Roadless areas across the National Forest System are among the last large places in the contiguous United States where these systems still function with relatively little human modification. Researchers describe primary forests — those with the least disturbance history — as having "the most developed dissipative structures, the highest levels of ecosystem processes, greater stability and recovery, and thus greater resilience and the lowest risk of loss and damage" (Rogers et al. 2022).

Fragmentation breaks these systems apart. A synthesis of habitat fragmentation studies spanning multiple biomes and continents found that fragmentation reduces biodiversity by 13 to 75 percent across studied ecosystems, with effects strongest in the smallest and most isolated fragments and intensifying over time. Globally, 70 percent of remaining forest is now within one kilometer of an edge — close enough that the buffering, cooling, and habitat-providing functions of intact interior forest are compromised. Fragmentation also impairs core ecosystem functions: reduced biomass, altered nutrient cycles, less carbon storage, less water retention (Haddad et al. 2015; Pardini et al. 2010). What's lost in a fragmented forest is not just species — it is the functioning of the system that the species were part of.

Roadless areas matter to ecosystem integrity in two ways. They retain the functioning systems that fragmented landscapes have lost. And they serve as reference landscapes — places where researchers can observe what intact systems actually do, providing the baseline against which degradation elsewhere is measured. Watersheds with the highest ecological integrity scores in the National Forest System tend to be dominated by wilderness and roadless area; watersheds with the lowest scores tend to have moderate road density and little roadless cover. Roadless areas also enhance the broader protected-area network by buffering existing protected areas from external disturbance and connecting them to each other across the landscape (Talty et al. 2020; USDA Forest Service 2000).

What the research shows

Fragmentation reduces biodiversity and ecosystem function together. A synthesis of habitat fragmentation studies spanning multiple biomes and 35 years found that fragmentation reduces biodiversity by 13 to 75 percent and impairs core ecosystem functions including biomass production, nutrient cycling, and carbon storage. Effects are strongest in the smallest and most isolated fragments and intensify with time (Haddad et al. 2015).

Most remaining forest is already fragmented. Globally, 70 percent of remaining forest is within one kilometer of a forest edge — within the zone where edge effects compromise interior conditions. The remaining intact interior, including roadless areas in the National Forest System, has become disproportionately important for sustaining the species and processes that require unfragmented forest (Haddad et al. 2015).

Intact forests provide ecosystem services that fragmented ones cannot. Primary forests with the least disturbance history have the highest carbon storage, the highest ecosystem-process levels, greater stability and recovery, and the lowest risk of loss. Connectivity, biodiversity, and microclimate buffering combine to give intact forests greater adaptive capacity in a changing climate (Rogers et al. 2022).

Roadless areas anchor the highest-integrity watersheds. Within the National Forest System, watersheds with the highest ecological integrity scores tend to be dominated by wilderness and roadless areas — over 50 percent roadless or wilderness cover in 81 percent of the highest-integrity subbasins. Watersheds with the lowest integrity scores show the opposite pattern: little roadless cover and moderate to high road density (USDA Forest Service 2000).

Roadless areas buffer and connect existing protected lands. Roadless areas are directly adjacent to protected areas on 58 percent of their land, expanding the six largest core protected areas in the lower 48 by an average of 25 percent. They also reduce isolation between protected areas and add representation of underprotected ecosystem types — including temperate grasslands and cool temperate forests — that the existing protected-area system does not cover well (Talty et al. 2020).

Sources

Show all 10 sources

Peer-reviewed research

  1. Rogers, B. M., Mackey, B., Shestakova, T. A., et al. (2022). Using ecosystem integrity to maximize climate mitigation and minimize risk in international forest policy. Frontiers in Forests and Global Change, 5, 929281.
  2. Hoffmann, M. T., Ostapowicz, K., Bartoń, K., Ibisch, P. L., & Selva, N. (2024). Mapping roadless areas in regions with contrasting human footprint. Scientific Reports, 14, 4722.
  3. Talty, M. J., Mott Lacroix, K., Aplet, G. H., & Belote, R. T. (2020). Conservation value of national forest roadless areas. Conservation Science and Practice, 2(11), e288.
  4. Chase, J. M., Blowes, S. A., Knight, T. M., Gerstner, K., & May, F. (2020). Ecosystem decay exacerbates biodiversity loss with habitat loss. Nature, 584(7820).
  5. Ibisch, P. L., Hoffmann, M. T., Kreft, S., et al. (2016). A global map of roadless areas and their conservation status. Science, 354(6318), 1423–1427.
  6. Haddad, N. M., Brudvig, L. A., Clobert, J., et al. (2015). Habitat fragmentation and its lasting impact on Earth's ecosystems. Science Advances, 1(2), e1500052.
  7. Pardini, R., Bueno, A. de A., Gardner, T. A., Prado, P. I., & Metzger, J. P. (2010). Beyond the Fragmentation Threshold Hypothesis: Regime Shifts in Biodiversity Across Fragmented Landscapes. PLOS ONE, 5(10), e13666.
  8. Saunders, S. C., Mislivets, M. R., Chen, J., & Cleland, D. T. (2002). Effects of roads on landscape structure within nested ecological units of the Northern Great Lakes Region, USA. Biological Conservation, 103(2), 209–225.

Government and technical synthesis

  1. USDA Forest Service. (2001). Forest Roads: A Synthesis of Scientific Information. Pacific Northwest Research Station, PNW-GTR-509.
  2. USDA Forest Service. (2000). Forest Service Roadless Area Conservation Final Environmental Impact Statement, Volume 1.

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