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Roadside Revegetation

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IMPLEMENTATION GUIDES<br />

most topsoil piles. Climates with lower moisture and temperatures can be more favorable to<br />

long- term storage. A study in Alberta, Canada, for instance, revealed that topsoil had very little<br />

respiration or organic decomposition after three years in a stockpile due to the influence of<br />

the cold, dry climate (Visser, Fujikawa, and others 1984). Dry topsoils store longer and maintain<br />

greater populations of viable mycorrhizal fungi (Miller and Jastrow 1992). If a topsoil pile is<br />

to be held over winter in areas of moderate to high rainfall, it should be kept dry by covering<br />

with plastic (which will also keep the piles protected from erosion and weed establishment).<br />

The size of the pile can also affect the viability of the topsoil. The interior of large piles<br />

maintains higher temperatures and are usually anaerobic, which can be detrimental to soil<br />

microorganisms. Microbial biomass levels and mycorrhizal fungi have been found to be very<br />

low in the bottom of large stockpiles (Ross and Cairns 1981; Miller and Jastrow 1992). Most<br />

projects limit topsoil piles to 3 to 6 ft in height. This is not always possible, especially when<br />

topsoil storage space is limited. Under these circumstances, the size of the topsoil pile can be<br />

quite large. To reduce the negative effects associated with very large piles, topsoils should be<br />

salvaged dry and kept dry during storage. Large piles should be stored for as short a time as<br />

possible. In addition to maintaining the viability of the topsoil, minimizing storage time will<br />

reduce the risk of weed infestation.<br />

Standard specifications often call for temporary seeding of topsoil piles. The benefits of this<br />

practice are erosion control and maintenance of mycorrhizae inoculum through the presence<br />

of live roots. This practice should be evaluated for each project to avoid the introduction of<br />

undesirable plant species in the seeding mix if non-native species are used. Alternatives to<br />

this practice include hydromulching without seeds or covering with plastic, however, both<br />

practices loose their effectiveness with time.<br />

Reapplying Topsoil<br />

The depth of topsoil application is generally<br />

based on the amount of topsoil<br />

Total soil nitrogen (or<br />

A other nutrient of interest)<br />

available and the desired productivity<br />

in salvaged topsoil<br />

of the site after application. As a rule,<br />

0.14 %<br />

the deeper topsoil is applied, the higher<br />

the site productivity will be. If the objective<br />

is to restore a site to its original<br />

productivity, the placement of topsoil<br />

should be at a depth equal to or greater<br />

B<br />

C<br />

Soil bulk density<br />

Fine soil fraction<br />

1.1<br />

70<br />

gr/cc<br />

%<br />

than the topsoil horizon of undisturbed<br />

Nitrogen for soil layer<br />

reference sites. Sufficient topsoil quantities<br />

however, are rarely available in the<br />

(A * B * C * 270) =<br />

Minimum or threshold<br />

quantities needed to restore disturbed<br />

N levels<br />

sites to their original topsoil depths.<br />

This often leads to applying topsoil too<br />

Minimum topsoil application:<br />

E/D<br />

thinly across a project site. There may be<br />

* 12 =<br />

a minimum topsoil depth below which<br />

the application of topsoil is not effective.<br />

Research on a northern California road construction site (Claassen and Zasoski 1994) suggests<br />

that a depth of 4 to 8 inches was required for an effective use of topsoil. On sites where the<br />

subsoil is unfavorable for plant establishment (e.g., very high or low pH, high sodium, high<br />

salinity), minimum depths of greater than 12 inches of topsoil should be considered (Bradshaw<br />

and others 1982).<br />

Determining minimum topsoil application depths can be based on the minimum amount<br />

of nitrogen required to establish a self-maintaining plant community. A threshold of<br />

approximately 700 kg/ha (625 lb/ac) of total nitrogen in the topsoil has been suggested for<br />

sustaining a self- maintaining plant community in a temperate climate (Bradshaw and others<br />

From soil test of post construction<br />

soils - reported in gr/l, ppm, mg/kg, ug/g<br />

divide by 10,000 for %<br />

Unless known, use 1.5 for compacted<br />

subsoils, 1.3 for undisturbed soils,<br />

0.9 for light soils such as pumice<br />

100% minus the rock fragment content -<br />

from estimates made from sieved soil<br />

prior to sending to lab<br />

D 2,911 lbs/ac ft Calculated amount of total nitrogen in<br />

1 acre feet of soil<br />

E 1,100 lbs/ac Determined from reference sites or<br />

minimum thresholds from literature<br />

F 4.5 inches The minimum thickness of topsoil to apply<br />

to meet minimum thresholds of nitrogen<br />

Figure 10-24 | Salvaged soil can<br />

be tested for nitrogen content<br />

Soil testing of salvaged topsoil can be<br />

used to calculate the thickness to apply<br />

in order to meet minimum nitrogen<br />

levels.<br />

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

253

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