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    Development of a Soil Erosion Classification Systemfor Cut and Fill Slopes

    David Hernando1 & Manuel G. Romana1

    Accepted: 8 June 2015 /Published online: 23 June 2015# Springer New York 2015

    Abstract The Universal Soil Loss Equation (USLE) has been widely used to predictthe long-term average annual soil loss associated with sheet and rill erosion caused byrainfall and runoff. Initially developed for agricultural purposes, it was later modifiedand extended for estimating soil loss on cut and fill slopes. In addition to this valuableequation, management of cut and fill slopes also requires a classification system inorder to prioritize erosion control measures and maintenance operations based onestimated soil loss. Currently available erosion classifications (focused on soil produc-tivity and sustainable agriculture) may not be relevant to transportation infrastructureslopes, in which soil loss rates are dramatically higher and primarily concern opera-tional service conditions. Therefore, the objective of this study was to develop aclassification system based on soil loss rates computed by the USLE model that canbe valuable for management of cut and fill slopes. It was assumed that erosionclassifications developed for agriculture could be used in cut and fill slopes as longas the ratio between respective soil loss rates was applied. It was found that thetopographic factor, which accounts for the length and steepness of the slope, mayexplain most of the difference in respective soil loss rates. For typical values of thetopographic factor, soil loss rates on cut and fill slopes were found to be roughly tentimes greater than those on agriculture. Based on this finding, a new classification withsix erosion levels was developed. Finally, validation analysis showed that the proposedclassification successfully ranked soil loss rates reported in the literature into differentcategories.

    Keywords Soil erosion . Universal Soil Loss Equation . Slopemanagement .

    Classification system . Cut and fill . Transportation infrastructure

    Transp. Infrastruct. Geotech. (2015) 2:155166DOI 10.1007/s40515-015-0024-9

    * David

    Manuel G.

    1 Department of Civil EngineeringTransport, Technical University of Madrid, Profesor Aranguren3, 28040 Madrid, Spain

  • Introduction

    Soil erosion is a major concern for its long-term effects on soil productivity, sustainableagriculture, and water quality. It is a problem of wider significance occurring addition-ally on land devoted to forestry, transportation, and recreation [1]. The Universal SoilLoss Equation (USLE) developed by Wischmeier and Smith [24] is the most widelyused equation for soil erosion analysis all over the world. It is an empirical model thatpredicts the long-term average annual soil loss associated with sheet and rill erosioncaused by rainfall and runoff:

    A RKLSCP 1where A is the long-term average annual soil loss rate (in units of mass area1 year1), Ris the rainfall erosivity factor, K is the soil erodibility factor, LS is the topographic factor(length and steepness of slope), C is the cover and management factor, and P is theconservation practice factor.

    Israelsen et al. [5] modified and extended the USLE model for estimating soil losspotential on cuts and fills of construction sites, resulting in the following equation:

    A RKLSVM 2in which A is the long-term average annual soil loss rate; R, K, and LS are those definedfor Eq. 1; and VM is the erosion control factor. Equation 2 was successfully applied toslopes up to 84 % [5], which are in the order of the slopes commonly found onhighways, railways, parking lots, and other construction sites. In addition to thisvaluable prediction model proposed by Israelsen et al. [5], management of cutand fill slopes requires a classification system such that erosion control mea-sures and maintenance operations can be assessed and prioritized according toestimated soil loss rates. Currently available erosion classifications focus on theconcept of tolerable soil loss, which is mainly related to the maximum rate thatcould occur indefinitely without adversely affecting soil productivity [1, 3, 6,7]. However, classification systems based on soil productivity may not begenerally applicable to evaluate soil erosion on transportation infrastructures,in which maintaining fully operational service is of paramount importance.Therefore, the objective of this study was to develop an erosion classificationsystem based on soil loss rates that can be truly valuable for management ofcut and fill slopes on highways, railways, and other transportationinfrastructures.

    Problem Statement

    Several classifications based on soil loss or soil removal have been reported in theliterature for sheet and rill erosion. Zachar [8] proposed six grades of soil removalintensity: insignificant, slight, moderate, severe, very severe, and catastrophic erosion,which ranged from 200 m3 ha1 year1

    (catastrophic). Wall et al. [9] defined five classes of potential soil loss ranging fromvery low or tolerable erosion (33 t ha1 year1).

    156 Transp. Infrastruct. Geotech. (2015) 2:155166

  • Morgan et al. [10] developed a classification to appraise soil erosion in the field thatranged from very slight (500 t ha1 year1). One ofthe most extensively used references in soil erosion classification was proposed byFAO-PNUMA-UNESCO [11]. This classification (Table 1) defined four erosion levelsbased on soil loss rates computed using the USLE model. Low erosion level wasdefined for soil loss rates 200 t ha1 year1.

    The aforementioned classifications were primarily developed for agricultureand may not be fully applicable to cut and fill slopes for two major reasons.First, concerns in slope management are not related to soil productivity, butoperational service conditions associated with deposition of sediments along theinfrastructure right-of-way. Eroded material accumulates on ditches, culverts,and sediment traps and may eventually reach the shoulder, constituting apotential hazard for infrastructure users. In addition, a clogged drainage systemmay result in overflow, washout, undermining, and collapse of earthworks andstructures [12, 13]. Secondly, soil loss rates on cut and fill slopes are reportedto be dramatically higher than those on agricultural lands. Navarro [14] statedthat soi l loss on construction sites typically ranges from 125 to600 t ha1 year1. Soil loss rates from 62 to 887 t ha1 year1 weremeasured on highway cuts in Georgia [15]. Haigh [16] reported values from373 to 426 t ha1 year1 in Oklahoma. Soil loss rates up to 248 t ha1 year1

    were measured on granitic cut slopes in Idaho [17]. In the Qinghai-Tibethighway (China), Xu et al. [18] found soil losses of 24 and 109 t ha1 forperiods of 28 and 78 days, respectively, which would be equivalent to averageannual rates of 310510 t ha1 year1. In Spain, rates from 79 to962 t ha1 year1 were predicted on slopes of highways and railways, as wellas peak values near 1100 t ha1 year1 under severe rainfall events [19, 20].

    As shown above, soil erosion on cut and fill slopes of transportationinfrastructures clearly exceeds the maximum soil loss rates defined by agricul-tural classifications. The approach followed in this study consisted of identify-ing the ratio of typical soil loss rates on cut and fill slopes to those onagricultural lands. It was assumed that erosion classifications developed foragriculture could be used in cut and fill slopes as long as the identified ratiobetween respective soil loss rates was applied. This ratio was the basis for thedevelopment of a new classification system based on soil loss rates estimatedaccording to the USLE model.

    Table 1 Level of erosion based onaverage annual soil loss rate foragriculture [11]

    Soil loss rate(t ha1 year1)

    Erosion level

    200 Very high

    Transp. Infrastruct. Geotech. (2015) 2:155166 157

  • Relationship Between Soil Loss Rates on Cut and Fill Slopes to Thoseon Agricultural Lands

    The factors contained in the USLE model (Eqs. 12) were analyzed in this section toestimate the ratio of typical soil loss rates on cut and fill slopes to those on agriculturallands. The following observations were made:

    & Rainfall erosivity and soil erodibility are prefixed by nature and cannot be alteredby human activities [5]. Thus, R and K factors are preset and do not necessarilydiffer between agricultural lands and cut and fill slopes.

    & The effect of land use and management on soil loss is taken into account by theterm CP in Eq. 1 and by VM factor in Eq. 2, respectively. For agricultural fields,CP includes crop type, tillage system, and support practices (e.g., contouring,contour stripcropping, terracing). For cut and fill slopes, Israelsen et al. [5] con-densed all erosion control measures that can be implemented on any cut and fillslope in a single factor (VM). Reported values for CP and VM suggest that landuse and management may not explain the substantial difference in soil loss ratesbetween agricultural lands and cut and fill slopes [4, 5].

    & Conversely, the topographic factor definitely presents distinct values because of thedifferent nature in length and steepness. Relatively flat slopes and long lengths arefrequent on agriculture, whereas steep slopes and short lengths are commonly used oncuts and fills.

    The above discussion led to the assumption that the dramatic difference in soil lossrate may be primarily explained by the different values in topographic factor. Thefollowing equation was given by Wischmeier and Smith [4] to determine the topo-graphic factor (LS):

    LS 22:13

    m 65:41sin2 4:56 sin 0:06