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Roadside Revegetation

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PLANNING PHASE TWO: ASSESS SITE<br />

penetrate the soil to access water. Soil structure is important for other soil functions such as<br />

air flow, drainage, permeability, infiltration, and essential habitat for most soil organisms. Soils<br />

with good structure are typically very productive.<br />

Soil structure is significantly reduced by operating heavy equipment over soils. The pressure<br />

applied by heavy equipment compacts the macropores, reducing soil volume and increasing<br />

soil density. This impact is called soil compaction (Figure 5-15). The effects of soil compaction<br />

on tree growth are well documented (Poff 1996). Trees growing on highly compacted soils have<br />

far less root, stem, and leaf production than those growing on non-compacted sites. Studies<br />

have shown a linear relationship between the increase in surface soil bulk density and decrease<br />

in height growth of young Douglas-fir and ponderosa pine trees (Froehlich and McNabb 1984).<br />

It should be assumed that soils will be highly compacted after construction due to the use of<br />

heavy equipment. In addition to reducing the potential of a construction site to grow vegetation,<br />

compaction also increases runoff and sediment during rainstorm events, which can impact<br />

water quality. On sites where summer rainfall is limiting, there will also be less water entering<br />

the soil, reducing the amount of water available for plant growth.<br />

Compaction can occur several feet below the soil surface, depending on soil texture, moisture,<br />

and the type and weight of equipment being operated. Very compacted soil layers can<br />

significantly reduce or eliminate root penetration. Where compacted layers occur, downward<br />

water movement is restricted and water may saturate the soil layers above the compacted layer.<br />

The resulting saturated soil conditions can be very restrictive to root growth because of the<br />

lack of oxygen and the propensity for higher incidence of disease (Steinfeld and Landis 1990)<br />

and seedling mortality (Figure 5-16). Compacted layers will naturally recover to their original<br />

porosity through root penetration, animal activity, and freeze-thaw events, but recovery can<br />

take 20 to 70 years (Wert and Thomas 1981; Froehlich and others 1983).<br />

Soil Structure – How to Assess<br />

It is easy to qualitatively differentiate good soil structure from compacted soil, but measuring<br />

it quantitatively can be difficult. Indirect field tests to quantify soil structure include bulk<br />

density and penetrometer tests.<br />

The bulk density test measures the dry weight of a standard volume of soil. If the soil has a<br />

high porosity, the bulk density values will be low; if the soil is compacted, the bulk density will<br />

be high. In this method, a cylindrical tube is driven into the soil with a portable bulk density<br />

sampler and a soil core is removed (Figure 5-17). The soil is shaved evenly on both ends so<br />

that the soil is exactly the shape and volume of the cylinder. The soil is then removed from<br />

the cylinder, oven-dried, and weighed.<br />

Bulk Density = weight of soil (g) / cylinder volume (cc)<br />

Bulk density values of a disturbed site must be related back to the bulk density of an adjacent<br />

reference site to make the values meaningful. Remaining within a 15 percent increase in bulk<br />

density over reference site values is ideal. Unfortunately, the bulk density method is time<br />

consuming and cannot be conducted on soils with high rock fragments.<br />

A less quantitative, but more practical, method of measuring soil porosity is with a soil penetrometer.<br />

This equipment measures soil strength instead of density. Compacted soils have<br />

greater strength, and greater resistance to penetration by a penetrometer, than non- compacted<br />

soils. Several types of penetrometers can be purchased for field work – penetrometers that<br />

measure the resistance as a continuous pressure is applied to the probe and penetrometers<br />

(impact penetrometers) that measure the number of blows of a hammer to drive the penetrometer<br />

into a specified depth. A monitoring procedure for assessing compaction using an<br />

impact penetrometer has been developed by the NRCS (Herrick and others 2005b). The most<br />

practical and economical field method for assessing compaction, however, is simply using a<br />

long shovel, as shown in Figure 5-18. In this method, a site is traversed and, at predetermined<br />

Figure 5-15 | Compacted soil<br />

Compacted soils are created by heavy<br />

equipment operating over soil. The<br />

large pore spaces are compressed and<br />

the impacted soils often form a platy<br />

structure as shown in this photograph.<br />

Figure 5-16 | Poor draining<br />

soils due to soil compaction<br />

Compacted soils drain very slowly,<br />

as the puddles on the surface of the<br />

obliterated road in this photograph<br />

indicate. During rainfall or snowmelt,<br />

soils can stay saturated for days and<br />

even weeks. Establishing seedlings<br />

during this period can be very difficult<br />

because roots cannot survive when soils<br />

are poorly drained. Seedlings shown<br />

in this photograph were dead within<br />

three months.<br />

Figure 5-17 | A soil core is used<br />

to determine bulk density and<br />

water-holding capacity<br />

<strong>Roadside</strong> <strong>Revegetation</strong>: An Integrated Approach to Establishing Native Plants and Pollinator Habitat<br />

71

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