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Riparian Restoration

CHAPTER 3: HOW RECREATION IMPACTS AFFECT KEY CHARACTERISTICS OF RIPARIAN ECOSYSTEMS (CONTINUED)

Soil and Vegetation Diversity (Continued)

Loss of vegetative cover, duff cover, and the subsequent loss of the organic horizon or topsoil by flooding and/or by continued human disturbance, such as trampling, exposes mineral soils. Furthermore, trampling frequently increases light intensities and temperatures, both above and below the soil surface (Cole as quoted in Alexander and Fairbridge 1999). Increased light intensity and temperature disturb the physical, biological, and chemical characteristics of the soil, resulting in lower productivity and lower water infiltration rates. See figures 38, 39, 40, 41, and 42.

Photo of a campsite with young trees dispersed sporadically through it.
Figure 38—Use at this dispersed site has isolated young trees.
The stump of one is visible.

Photo of a bare ground site that has sporadic cover of short leafy vegetation and bushes.
Figure 39—An ever-expanding dispersed site.

Photo of a large puddle in the middle of a wide trail that cuts through a forest.
Figure 40—This Alaskan trail is in a rain forest, so it is always
wet. Hikers walk on the edges of the trail, trampling plants,
ever widening the trail, and exacerbating the problems.
The trail is also compacted, muddy, and rutted.

Photo of a small parking lot set by a stream. The bank of the stream is vegetated with grass and brush, except for an eroded gouge located by the parking lot.
Figure 41—This dispersed parking lot is growing because there
are no boundaries. The vegetation is becoming more and more
trampled. Angler access to the river has caused a large chunk
to erode. High flows eventually will cause further erosion
at this vulnerable spot.

Photo of a lakeside parking lot with cars parked at the edges of it.
Figure 42—Windfall Lake Trailhead. There is no defined boundary
and therefore no edge to this parking area. Parking areas with no
boundaries expand when they become crowded or as drivers
seek to park under shade.

Pore spaces in the soil aerate roots and hold water. Compaction packs the soil particles closer together and eliminates pore spaces (Cole as quoted in Alexander and Fairbridge 1999). Compaction allows less infiltration, which leads to lower soil moisture content, fewer seeds germinating, and lower rates of seedling survival. “Young and Gilmore (1976) found that even when relatively high levels of organic matter and soil nutrients were present, they may be unavailable, perhaps due to high soil compaction and low soil moisture and oxygen content” (Manning 1979). Reduced or eliminated pore space also weakens plant vigor and reduces root penetration. Compaction also decreases soil-building plant litter and the number of arthropods, earthworms, and beneficial bacteria and fungi present (Ferren and St. John 2000).

The following diagram illustrates the cumulative effects caused by trampling and treading as vegetation is weakened and soil is compacted. See figure 43.

Diagram that illustrates the negative effects trampling has on soil and vegetation.  Arrows interconnect the effects, showing how one effect can cause other consequential effects.
Figure 43—Soil/vegetation impact diagram (Manning 1979).

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