Experimental Assessments of Treating Effect on Retaining Walls for Loess Slopes under Long-Term Rainfall

Abstract

Failures of treated slope occurring in China are at a continually increasing rate, and the huge number of treated loess slopes is calling for a postevaluation; however, no mature technique is in place. Based on an actual loess slope in Shaanxi Province treated by retaining wall, indoor geotechnical and model tests were conducted, revealing the rainwater infiltration process and pressure variations behind the wall, and the processes were then adopted to perform the postevaluation of the treated slope. The results proposed that effectual measures hence needed to be taken so as to avert rainwater infiltrating along the wall face and back or flowing through the wall body, which can soften the soil of the slope bottom. Although the wet front was developed by the rainfall process, it cannot be used as the boundary between saturated and unsaturated areas. Despite the peculiarly large soil pressure upon the wall back at the top layer, the soil pressure increases to a large value and then decreases with the depth. The model test results and investigation results were used to conduct the postevaluation of the prototype slope, which formed a postevaluation frame relevant to other slope postevaluations.

This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

1. Introduction

Loess characterized by large porosity and water sensitivity forms a great number of slopes in the northwest of China, including natural slopes and artificial slopes [1]. Limited by the shortcomings of engineering technology of China in the last century, most of the artificial slopes in northwest China cannot guarantee ample safety after approximately a century of operation, especially for slopes treated by retaining walls. Consequently, the treated loess slopes collapsed generally in northwest China this century, which has caused serious life-threatening casualties to the adjacent people [2–7]. Thus, the artificially treated loess slopes distributed in northwest China need a remedial approach to prevent them from collapsing. This posed a new researching issue, namely, postevaluation of treated slopes, that differs from safety evaluation in project designing [8–10].

In the postevaluation of slopes, the researcher’s focal point is on the operational situation of the project, described by the characterization of the slopes such as the surface cracks, displacements, and adaptations to the environment [11, 12]. In view of the deficiency of the aforementioned qualitative analysis, some analysts set in motion stress evaluation methods into the slope treatment effect assessment [13]. Apart from their promoting effects to the current field, these developed assessment methods all fell into the limited range of qualitative or semiquantitative evaluation, without considering the long-term rainfall effects. Referring to the postevaluation, this issue must be a long-time operation problem without giving consideration to long-term rainfall [14].

These years, more researchers devoted themselves to the field of slope stability and failure mechanism study under rainfall, involving modelling test [15–20], numerical simulation [21–24], and field monitoring [25–27]. As investigated, slope safety is mostly influenced by rainfall, causing the surface erosion to the slopes by runoff [28–32], weakening the slope soil strength while percolating into the slope body [33–37], and reducing the effective stress in the slope soil while saturating the slope body [38–42]. For the soil slope is loose, especially for the loess slopes, the raindrops and the runoff water can easily scour the soil particles on the slope surface, in due course forming gullies and fall-holes in the slopes [43]. To alleviate the scouring by rainwater runoff, the vegetation covering method and geobarrier system were proposed by some scholars, ascertaining that both methods are capable of protecting the soil slopes from rainwater scouring and maintaining the stability of the slopes [44]. Consequently, the suction in the soil contributes significantly to the strength of slope soil. This is a crucial factor in slope stability [45]. As the rainwater percolates into the slopes, mainly for the slope with cracks on the slope surface, the water content of the slope soil increases, inducing the dropping of the suction, even causing the lifting of the groundwater level, which may eventually lead to the collapse of the slope [46]. Additionally, as a positive factor to the frictional strength of the soil, the effective stress favorable to the slope stability decreases with the increase of the pore water pressure in the rainfall process [47]. Evidently, rainfall has been a critical factor in the instability of slopes. In the circumstances of practical engineering, water drainage measures should be the obligatory practice to any project to alleviate the hazards of rainwater percolating.

The most direct and convictive method to study the slope stability (or slope treating effect) and failure mechanism is by model test, taken on by many researchers. Song and Tan [48] made use of the model test to study the influence of different slope surface covering on failure mechanism under intense rainfall. The results indicated that the slope with a bare surface is most prone to failure, with a sudden slide failure of the linear sliding surface. Hojat et al. [49] adopted a laboratory model test to study the exert influence of the rainwater infiltrating process on the slope sliding. As stipulated, the landslide body became unstable when the water saturation exceeded 45%, and the sliding surface was consistent with the interface of different saturation areas. Chueasamat et al. [50] used a 1 g slope model to investigate the failure mechanism of slopes composed of two different soil layers under different rainfall intensities. It indicated two different types of failures: videlicet surface sliding failure and retrogressive failure. Tohari et al. [51] incorporated the slope model into the study and ascertained that, under the rainfall condition, the localized failure surface is noncircular with nearly saturated water content, while the overall instability area retained unsaturated. The rainwater percolating process in the soil slope was studied by Park and Song [52] who found that the rainwater firstly concentrated at the slope toe forming a saturated zone near the slope toe advanced toward the slope crest. The sliding failure ensues in the saturated area.

From the above, the preceding research studies are mainly attentive to the pre-evaluation of slopes (aiming at design), while some limited amounts of postevaluation researching results are based on rock slopes or without treatment. Taking China’s loess slopes into account, there is hardly any research results of this aspect under the rainfall condition. In view of the great number of treated slopes in northwest China operated for a long time, this issue has been a research subject that needed to be commenced urgently.

Employing a model flume in the ongoing research, a retaining wall-treated loess slope model shrunk by 10 times from the prototype was constructed in the laboratory to scrutinize the treating effect of the retaining wall on this slope. Also, the rainwater infiltrating process, pore water varying process, and soil pressure upon the wall back were monitored, which would dispense some illustration to the effects of rainfall on the degradation of the treated loess slope. The sections of this paper below depict the regime of the model test and the results of the test, followed by the treating effect evaluation (postevaluation) incorporating the test results. The formed approach of the treating effect evaluation for retaining wall-treated loess slope can be relevant to other slopes, while the obtained rainwater infiltration and soil pressure variation rules can be adopted to facilitate the design and maintenance of the retaining wall-treated slopes.

2. The Prototype Failure

The slope prototype is situated in Zhangwan Village, Diantou Town, Huangling County, Yan’an City, Shaanxi Province, as shown in Figure 1. The geographical coordinates of the project are 109°05′46.92″E and 35°38′3.55″N, with an average elevation of 970 m. It consists of a temperate continental monsoon climate, with an annual average temperature of 9.4°C and an annual utmost maximum temperature of 39.4°C. The average annual precipitation of Huangling County is approximately 690.2 mm, briefly concentrated in July, August, and September.

[figure omitted; refer to PDF]

Located on the loess plateau, the current project is a loess slope treated by a stone gravity retaining wall with an uphill road on the crest. That is, the soils behind the retaining wall are wholly loess formed in the late Pleistocene epoch. As Figure 2(a) shows, the height of the slope is 8.6 m, the back of the retaining wall is vertical, the slope of the retaining wall surface is 70°, and the width of the retaining wall top is 55 cm. From this, the retaining wall width at the height of the slope toe is 3185 cm.

[figures omitted; refer to PDF]

From field investigation and datum collection, this project was built around the year 2012, having been operated for virtually 5 years when the field investigation was performed. After a long period of operation degrading by the rainfall, the retaining wall was found extruded in the middle height of the slope (see Figure 2(b)). To make the postevaluation for this project by modelling test, the simulated time must be 5 years depending on the actual project operation time frame. Pursuant to the similarity theory, the test time can be shortened 100 times, and thus, this model test can be completed in a more tolerable period of time.

3. Methodology and Test Model

3.1. Test Device

The rainfall test was conducted in the Soil Mechanics Laboratory of Shangluo University, China. A box of 1 m in width, 2.5 m in length, and 1.8 m in height was adopted in the experiment (see Figure 3(a)). The left and right side walls of the box were made from organic glass, making the displacement of the slope soil and the wetting front visible. The base and the back wall of the box were made from plank, and the front of the flume was blocked by a plank of 30 cm height while the upper plank of the front could be removed to let slope surface unrestrained. To vent the rainwater infiltrated into the slope, holes were drilled in the lower 30 cm high front plank.

[figures omitted; refer to PDF]

A frame made from steel pipes with holes of 1 mm in diameter was used as a rainfall simulator with the rainfall intensity controlled by the valve connected to the water pipe (see Figure 3(b)). Prior to the rainfall, the rainfall intensity must be calibrated to the desired values, which were measured by a beaker and a measuring cylinder.

3.2. Test Model

The test model corresponded fully to the prototype characteristics of the slope in Zhangwan Village, Diantou Town, Huangling County, Yan’an City, Shaanxi Province, as illustrated in Figure 1. The scale of the model was 1 : 10, and thus, the model height was 0.86 m, the length of the model was 2.5 m consistent with the length of the model box, while the front 1.08 m was just 30 cm thick and horizontal. The retaining wall was constructed from stones and mortar with a slope of 70° also consistent with the prototype. Shrunk by 10 times from the prototype, the width of the model wall top was 5.5 cm and the width of the model wall bottom was 17 cm. The detailed dimensions of the test model are shown in Figure 4.

[figure omitted; refer to PDF]

The slope prototype was firstly sampled as undisturbed samples, and the density, water content, grain size distribution, permeability, and shear strength of which were determined by indoor experiments. Dependently, the model material was the same loess procured from the project prototype site. The model was constructed by stratified compaction. To control the mode slope soil density and water content, the mass of each layer of 10 cm thick was weighed and the model soil was prepared to certain water content in advance. The retaining wall was constructed synchronously with the slope soil.

As Figure 5 illustrates, the model construction process is considerably complicated and can be delineated as follows:

(1) The M5 mortar and stone (average diameter≈15 cm) were prepared and were used to build the retaining wall. As every 10 cm high wall was built, a form was adopted to support the wall against falling.

(2) Synchronously, the procured loess was prepared with precise water content as the prototype (ω = 17.4%) and packed into the model box with a certain quantity as a layer, and then each layer was compacted to a thickness of 10 cm to control the density of the slope model.

(3) Steps 1 and 2 were repeated until the slope was built to the predetermined height.

(4) In the model construction process, the pore water pressure sensors and soil pressure sensors were buried in the designed position. As the model construction process was over, the model was left to stand for 2 days until the mortar solidified

(5) Lastly, the displacement measuring positions were marked on the wall face by a mark pen.

[figure omitted; refer to PDF]

To measure the displacements of representative points, 5 key points were marked by a mark pen on the retaining wall face, which are also illustrated in Figure 7 as S1, S2, S3, S4, and S5 sequentially. S1 was located on the shoulder of the wall, while S2 was located on the wall face with a vertical distance of 20 cm from S1, and S3, S4, and S5 were also positioned on the wall face with a vertical distance increment of 20 cm sequentially. Visibly, S2, S3, S4, and S5 were at the same elevations as P1, P2, P3, and P4, respectively. The displacements of the 5 points were derived from the differences of distances before and during rainfall, which were measured by a laser rangefinder constantly seated in a fixed position. The accuracy of this laser rangefinder is up to 0.01 mm which could satisfy the measuring requirement without any doubt. Conveniently, the laser rangefinder was also connected to the computer to display the distance values.

To capture the deformation process of the retaining wall and the rainwater penetrating process in the slope, a portable camera was adopted to take photos from the front as well as the sides of the model at constant intervals.

As aforementioned, the annual precipitation of Huangling County is approximately 690.2 mm, mainly concentrated in July, August, and September. In this study, we assumed the total annual precipitation distributed in the above three months, with every month consisting of a one-time rainfall lasting 2 hours. After the rainfall, the slope was remained undisturbed for the remaining time of the month. Thus, the 2-hour rainfall intensity was constantly 115.03 mm/h. The rainfall intensity in the model test could be derived from dividing 115.03 by the similarity constant of $\sqrt{10}$, resulting in the model test rainfall intensity value of about 36.38 mm/h. More importantly, the total test period could be derived from dividing 5 years by the similarity constant of 100 (see equation (5)), deducing a value of 0.05 years, i.e., 18 days, while the undisturbed intervals between the 3 times of model test rainfall could be derived from dividing 30 days by the similarity constant of 100 then subtracting 2 hours, deducing a period of 5.2 hours. The detailed rainfall scheme of a year is presented in Table 3, which could be repeated 5 times to simulate 5 years of rainfall.

Table 3

The rainfall scheme.

Simulating time	Actual time	Rainfall start	Rainfall end	Read data
0 h	0 h	Yes		Yes
2 h	2 h		Yes	Yes
7.2 h	30 d	Yes		Yes
7.2 h + 2 h	30 d + 2 h		Yes	Yes
14.4 h	60 d	Yes		Yes
14.4 h + 2 h	60 d + 2 h		Yes	Yes
21.6 h	90 d			Yes
28.8 h	120 d			Yes
36 h	150 d			Yes
43.2 h	180d			Yes
50.4 h	210 d			Yes
57.6 h	240 d			Yes
64.8 h	270 d			Yes
72 h	300 d			Yes
79.2 h	330 d			Yes
86.4 h	360 d			Yes

Generally, the experimental process followed the steps below:

(1) The initial values of the pressure sensors were measured before they were buried as the building of the model

(2) After the model was built, the sensor cables were connected to the strainometer which was connected to a computer to capture the pressure data. Simultaneously, the laser rangefinder was fixed at a position and connected to the computer to get the distances between the position and the displacement points (S1, S2, S3, S4, and S5), thus deriving the displacements of the 5 points.

(3) The rainfall intensity of the rainfall simulator was calibrated to the value of 36.38 mm/h and then acted on the model slope surface as the pressure capturing program started.

(4) Following the steps of Table 3, the rainfall process was progressed while the pressure values were captured by the program and the rainwater infiltration process was captured by the camera from the front and sides.

4. Rainwater Infiltration Characteristics

Slope soil can be saturated by rainwater infiltration, thus increasing the pore water pressure or lessening the suction in the slope body, which significantly affects the slope stability. For retaining wall-treated slopes, the infiltrated rainwater would reduce the internal friction angle of the slope soil, thus causing the significant increment of active earth pressure on the wall back which is adverse to the treating project. Additionally, the infiltrated rainwater accumulated behind the wall, causing the large water pressure on the wall back which is adverse to the stability of the project. Some scholars took the influence of rainfall on the slope stability into account and made discoveries that the rainfall was the most significant factor controlling the stability of slopes and the rainwater infiltrating process dominates the deforming process of slopes [48, 50]. In this study, the two side walls of the model box were made of transparent organic glass. Thus, the rainwater penetration process could be captured by the cameras from the sides.

4.1. Rainwater Infiltration in front of the Wall

Figure 8 presents the wetting front advancement as the rainwater penetrates in front of the retaining wall in the first year of rainfall. Owing to the fact that the loess in front of the retaining wall was completely wet 5.2 hours after the first rainfall of the first year, the wetting process of the loess in front of the wall subsequent was not visible and consequently not presented here. It is crystal clear that the rainwater preferentially penetrates along the interface between the retaining wall and the front loess. That may be due to the insufficient connection between the loess and the retaining wall face, which could be aggravated, causing the erosion effect of the rainwater or the displacement of the wall. Propelled by the matric suction of the loess, the infiltrated rainwater migrated forward, causing the wet range of the front loess to expand. When the first rainfall of the first year lasted for 20 minutes, the length of the wet range in front of the retaining wall was approximately 25 cm. As the rainfall continued for 60 minutes, the wet range in front of the retaining wall approached 40 cm length which approximated 51 cm when the rainfall lasted for 120 minutes. Lastly, the rainwater completely wet the loess in front of the wall 5.2 hours after the first rainfall of the first year. Consequently, we could therefore derive that, during the rainfall, the horizontal expanding rate of the wetting front in front of the retaining wall was approximately 2.08 × 10⁻² cm/s which gradually decreased to 3.06 × 10⁻³ cm/s when the rainfall conducted for 120 minutes. However, the wetting front expanding rate in front of the wall after the rainfall was approximately 3.04 × 10⁻⁴ cm/s, close to the saturation permeability coefficient of the loess (see Table 1), possibly indicating the saturated status of the soil in front of the wall. Different from the permeating law of unsaturated soil, as the migration of rainwater progressed, the matrix potential of the soil decreased, thus leading to a decrease in the migration rate of rainwater.

[figures omitted; refer to PDF]

From the wetting front advancing process, it can be deduced that although the rainwater accumulated upon the surface of the front loess, the wet area expanding process in front of the retaining wall was mainly dominated by the rainwater penetrated along the interface between the retaining wall and the front loess. That should be attributed to the larger horizontal permeability caused by the layered filling of the slope while the impedance of the interface between the soil layers hinders the rainwater infiltrating vertically. Additionally, after the rainfall, the wetting area kept expanding which was induced by the suction of the loess, causing the dry area to narrow into a dot and disappear lastly (see Figure 8(e)). Consequently, we can infer that measures to avert the rainwater to penetrate along the interface between the retaining wall and the front loess can be effective and efficient ways to alleviate the softening of the front loess, thus preventing the disruption of the wall.

4.2. Rainwater Infiltration behind the Wall

Figures 9 and 10 present the wetting front advancement as the rainwater penetrates behind the retaining wall. It was observed that the loess behind the retaining wall was almost completely wet 70 hours after the third rainfall of the second year, and thus, the rainwater infiltration process subsequent was not visible and not presented here. It is clear that the rainwater preferentially penetrated along the interface between the retaining wall back and the loess likely due to the same reason as the rainwater penetration in front of the wall, while a considerable amount of rainwater flowed through the pores of the retaining wall body and accumulated at the wall back especially the wall heel. Propelled by the matric suction of the loess, the infiltrated rainwater migrated backward, causing the wet range of the back loess to expand. As the rainwater flowed down along the wall back, most of the penetration rainwater accumulated around the wall heel, and the wet range of the model bottom expanded much quicker than that of the upper part.

[figures omitted; refer to PDF]

[figures omitted; refer to PDF]

Within the first year during the beginning of the first rainfall, the rainwater penetrated the retaining wall pores and accumulated at the wall back, inducing the discontinuous wet area behind the wall. Presumably, this discontinuity is the result of the discontinuous pore in the retaining wall which inlets rainwater independently forming wet areas behind the wall. As the rainfall process advanced, more and more rainwater penetrates the wall leading the wet areas behind the retaining wall to gradually integrate. Because the rainwater mainly concentrated at the foot of the slope, the rainwater penetrated the wall bottom was more than that penetrated the upper part, thus causing the wider wet area at the wall heel. Thus, the wet area behind the retaining wall showed trapezoidal distribution during the first rainfall of the first year. When the first rainfall of the first year was conducted for 120 minutes, the width of the wet trapezoid top was about 11 cm and the width of the bottom of the wet trapezoid was about 31 cm. Approximately the rainwater horizontal infiltration rate in the loess at the retaining wall heel was 4.3 × 10⁻³ cm/s. Meanwhile, the vertical infiltration rate of the rainwater at the slope crest showed uniform distribution. When the first rainfall of the first year was conducted for 120 minutes, the rainwater infiltration depth at the slope crest was about 12.5 cm, deriving a vertical infiltration rate of about 1.74 × 10⁻³ cm/s. By comparison, the horizontal infiltration rate was clearly higher than the vertical infiltration rate, which is consistent with the conclusion of Gvirtzman [59]. 5.2 hours after the first rainfall of the first year, the 30 cm thick loess of the model bottom was wet, and the upper wet area showed rectangular distribution, which was caused by the horizontal migration of the more rainwater accumulated at the heel of the wall. Therefore, we can infer that rainwater is more prone to accumulate at the retaining wall heel, which can degrade the strength of the soil behind the wall, thus clearly affecting the stability of the retaining wall. If effective measures are adopted to prevent the rainwater to penetrate the wall body, especially the wall bottom, the retaining wall can more effectively protect the slope for a much longer time.

Visibly, the wetting front was clear just after the rainfall (see Figure 9(e)), but obscure 5.2 hours later (see Figure 9(f)) with the expansion of the wet area causing a decrease in the water content in the wet area. As seen, the width of the wet rectangle behind the retaining wall was about 27.5 cm when the second rainfall of the first year was conducted for 120 minutes but was 34 cm 5.2 hours later. With the advancing of the rainfall thereafter, the wet rectangle behind the retaining wall expanded continuously and the wet area at the slope crest developed downward, in due course took up the whole slope body (see Figure 10(d)). However, we can infer that the wet area behind the retaining wall could not represent the saturated area because the water in this area was distributed by the matric suctions. It means the slope soils did not get other water from outside to fill the soil pores, and thus, the visible wet area developed was inferred not saturated.

5. Pressure Variations of the Model Slope

The retaining wall stability is directly correlated with the pressures upon the wall back, inclusive of the soil pressure and the pore water pressure. Theoretically, in the rainfall process, the soil pressure and the pore water pressure upon the wall back to some extent increase. In a case where the increment of the pressure exceeds the limit, the wall may as a result extrude or incline, indicating the instability of the wall [60]. In this study, before the start of the rainfall, different pressure coefficients depending on the descriptions of the sensor were set in the capturing program. In accordance with this, the capturing program can automatically convert the signals sent by the strainometer into pressure, from which the actual pressure can be procured by subtracting the initial pressure values.

5.1. Pore Water Pressure Variations

The variations of the pore water pressures of the 5 representing points (U1, U2, U3, U4, and U5) with time are presented in Figure 11. As addressed earlier, the annual precipitation is concentrated in three months while the remaining months of the year are with no precipitation. To be operatable, the rainfall of each month was concentrated in 2 hours with an incessant intensity. Evidently, during the 3 months of rainfall, the pore water pressure of the 5 points fluctuated acutely, with a general trend of increasing during raining and declining within the rainfall intervals. In the months without rainfall, the pore pressure of the 5 points was observed to be constant with negligible fluctuations. That is, the migration of water in the slope body led to little variation in the suction, which can be explained by the hysteresis phenomenon of the soil-water characteristic curve, by which the great change of water content induces little suction change in the dry condition. However, all the pore pressures presented in Figure 11 were negative and only the pore pressure of U5 increased from a negative value to about 0 kPa, which indicated the saturated status around point U5. As depicted in Figures 9 and 10, the rainwater preferentially accumulated at the heel of the retaining wall, which led to the saturation of the soil around point U5, inducing a pore pressure value of about 0 kPa of U5. As delineated by Chueasamat et al. [50], the rainwater mainly concentrated at the slope toe, seeming consistent with this study at the heel of the retaining wall. Depending on Fredlund and Rahardjo [61] unsaturated soil theorem, the negative pore water pressures in the soil implies suctions, thereby indicating the unsaturated status of the soil. Thus, we can infer that the soils around all the five points except U5 were unsaturated in the 5 years of simulation. Therefore, we can come to a conclusion that although the wetting front passed the whole slope body, parts of the slope soils behind the retaining wall were retained at unsaturated status.

[figures omitted; refer to PDF]

Additionally, we can find from Figures 7 and 9 that point U4 was close to the interface between the saturated and unsaturated areas, and thus, the pore water pressure of U4 was mostly influenced by the rainwater infiltration, increasing from about −16 kPa before the rainfall to about −14 kPa at the end of the fifth year. However, point U4 was situated above the saturated area, and the pore water pressure there could not increase to a positive value. Also, the pore water pressures of points U2 and U3 gave no obvious variation, especially U3, indicating the soils below the depth of 20 cm were not efficaciously affected by the rainfall. In most situations as simulated in the present study, the rainfall duration is limited, causing no deeper infiltration of rainwater, which is minified by the evaporation in the rainfall intervals. That was consistent with the practical project experience that the rainfall can merely influence the water content of the top 2∼3 m thick layer of soil.

The pore water pressures with the depth at the end of the five years are presented in Figure 12. Because the permeability of the retaining wall varies irregularly, leading to the irregular variation of wetting extent of the soils along the wall back, the suction (negative pore water pressure) behind the wall showed no regular variation with depth, rather with a maximum suction value slightly above the saturation face. Accordingly, the most obvious variation of the suction with time was at the point sightly above the saturation face, which is due to the most drastic variation of water content near the saturation face in the rainfall process.

[figure omitted; refer to PDF]

According to the theorem of active soil pressure upon wall back for unsaturated soils proposed by Sahoo and Ganesh [63], the active soil pressure upon the wall back can be delineated as$$\begin{array}{}\text{(7)}& E_a=\frac{1}{2}\gamma H^2{K}_a.\end{array}$$

Here, K_a is the active soil pressure coefficient considering the matrix suction, the value of which is between 0.3 and 0.35 under the condition of rainfall according to the literature [63]. γ is the unit weight of the soil, c is the cohesion of the soil, φ is the internal friction angle of the soil, and H is the wall height. According to Table 1, the parameter ρ = 1.42 g/cm3, φ = 27°, and c = 15.0 kPa. Thus, γ = ρg = 14.2 kN/m3, K_a = 0.3∼0.35. Substituted these parameter values into Equation (7), we derived E_a = 286.61∼334.38 kN.$$\begin{array}{}\text{(8)}& R_t=\frac{F_t}{E_a}=\frac{172.6}{286.61\sim 334.38}=0.52\sim \mathrm{0.60.}\end{array}$$

According to Table 4, the treating effect of the prototype project in this preliminary evaluation section should be good.

7.4. Evaluating Results and Postevaluation Frame

Conservatively, to guarantee the correctness of the evaluation process, synthesizing the above evaluating results, the treating effect of the project should be good.

Lastly, it is noteworthy that the postevaluation frame formed in this paper is essential to be adopted in other slope treating projects that employed retaining walls. Thus, this evaluation frame is delineated in Figure 18.

[figure omitted; refer to PDF]

8. Conclusion

To divulge the influence of long-term rainfall on the loess slope situated in Yan’an City of Shaanxi Province treated by retaining wall, field investigations, and indoor model tests were performed, the results of which were adopted to conduct the postevaluation of the retaining wall treating project of the slope. The following conclusions were therefore obtained:

(1) The rainwater preferentially penetrates along the interface between the front soil and the retaining wall and accumulates at the slope toe. The accumulated rainwater then migrates forward horizontally and gradually submerses the whole front soil, softening the front soil which is adverse to the stability of the retaining wall. Thus, effective measures should be taken to prevent the rainwater from penetrating along the interface between the front soil and the retaining wall, alleviating the failure disaster to the retaining wall.

(2) Behind the retaining wall, the rainwater penetrates preferentially along the wall back, associating with the penetration of rainwater through the wall body. The penetrating rainwater accumulates mostly at the heel of the retaining wall, forming the larger width of wet area at the bottom of the slope, consequently softening the soil there, which is unfavorable to the safety of the retaining wall. Thus, effective measures should be taken to prevent rainwater from penetrating along the wall back and through the wall body.

(3) Even though the whole slope body is submersed during the rainfall process, the pore water pressures behind the retaining wall retain negative or zero, implying that the soil here is unsaturated.

(4) In the first year, the soil pressure upon the wall back at the intermediate height of the slope had a weakly visible increase, while the other positions hardly have variation. In the third year and thereafter, the soil pressure upon the wall back at the upper layer increases wildly, while the other positions remain unchanged. Regardless of the peculiarly large soil pressure upon the wall back at the top layer, the soil pressure increases to a considerable value and then drops with the depth along the wall back.

(5) In the first two years, the horizontal displacements of the retaining wall increased visibly and then retained with no regular variation with time. For this special project, at the end of the five years, the retaining wall has an obvious extrusion at the intermediate height of the slope, which is consistent with the investigation results.

(6) The above results were adopted to perform the postevaluation of the retaining wall treating project of the slope, which structured the frame for the postevaluation of retaining wall treating loess slope under long-term rainfall (see Figure 18). This evaluation frame can be valuable to other slope treating projects.

Acknowledgments

This research was financially supported by the Key R & D Program of Shaanxi Province (2018GY-099) and the Key R & D Program of Shangluo City (2020-Z-0111). The authors are very grateful to professor Wanjun Ye from for his help.

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