Mediumtolowspeed freight rail transport induced environmental vibration and analysis of the vibration isolation effect of building slope protection piles
Chenglong Sun^{1} , Liang Gao^{2}
^{1, 2}School of Civil Engineering, Beijing Jiaotong University, Beijing, China
^{1}Energy Saving and Environmental Protection and Occupational Safety and Health Research Institute, China Academy of Railway Sciences, Beijing, China
^{2}Corresponding author
Journal of Vibroengineering, Vol. 19, Issue 6, 2017, p. 45314549.
https://doi.org/10.21595/jve.2017.18168
Received 11 January 2017; received in revised form 16 August 2017; accepted 4 September 2017; published 30 September 2017
JVE Conferences
The environmental vibration induced by freight rail transport has become an important type of environmental pollution. The environmental vibration caused by a running freight train near a typical medium to low speed railway in China and in the surrounding residential area is measured and analyzed. The test result shows that in the region adjacent to the railway, the weighed vibration acceleration level as a function of time ($t$) in the vertical direction ($V{L}_{z}$) is lower than 80 dB, which meets the requirements of the standard (GB1007088); however, in the surrounding residential area, the $V{L}_{z}$ is in the range of 5874 dB, which is 04 dB higher than the specified limit during the day and 02 dB higher than the specified limit at night. For the isolation of environmental vibration induced by the freight train, a dynamic model of the vehicle and track and a finite element model of the railway, stratum and building are constructed to analyze the feasibility of modifying the slope protection piles outside of the building to make them function as vibration isolating piles, and the vibration isolation effects of such piles in a single row and double rows are compared with the case without piles. The simulation result shows that vibration isolation piles can attenuate the vibration level in front of and behind the piles: compared with the case without piles, the $V{L}_{z}$ can be reduced by 24 dB within 5 m behind the piles in a single row, and can be reduced by 410dB behind the piles in double rows, so the doublerow setup is recommended for vibration isolation. It is suggested that for residential buildings which are close to the existing medium to low speed freight railway lines and for which other vibration attenuation measures are impractical, satisfactory vibration isolation effects may be achieved by simply increasing the number of rows of slope protection piles.
Keywords: freight rail transport, environmental vibration, vibration isolation, piles in row, the weighted vibration acceleration level in the vertical direction.
1. Introduction
Rail transport has become the main mode of transportation for goods because of its large volume, small pollution, and safety and reliability. With the development of highspeed railway in China, the share of passenger transport by highspeed railway is gradually increasing. In contrast, the share of passenger transport by both medium and lowspeed railway has been decreasing year by year, and gradually shifted from mixed passengerfreight transport to freight dominated transport. However, because freight trains have large axle loads and dynamic parameters different from those of passenger trains, the environmental vibration induced by freight trains is more severe and the degree of annoyance is much larger than that of passenger trains. Sharp et al. [1] confirmed this by testing and investigating the relationship between the environmental vibration induced by both freight and passenger trains and human annoyance. Consequently, the number of complaints related to the environmental vibration is increasing in the vicinity of these freight railways. Therefore, it is necessary to study and control the environmental vibration caused by the existing freight trains.
Extensive studies have been conducted on the environmental vibration induced by rail transport. Kirzhner et al. [2] treated the train load, foundation soil and ground buildings as a whole, and computed and analyzed the effect of one vibration isolation measure the effective thickness of the replacement soil using a two dimensional model. Zhang et al. [3] established an excitation function for the vibration load of a train running on elevated urban transit railways, and proposed a formula to predict the level of environmental vibration adjacent to an elevated urban transit railway based on finiteelement simulation of the track supporting structures and soil. Ma et al. [4, 5] described the difference between the vibration signals detected at two measuring points inside and outside a building, respectively, and in different frequency bands, quantitatively predicted the influences of railtransit induced vibration on the human and precision instruments inside buildings. Xia et al. [6] constructed a theoretical model based on the dynamics of the coupling between the train, railway and bridge, more accurately reflecting the whole process from the generation to the transmission of vibration. The abovementioned studies mainly focused on the environmental vibration of passenger trains and its impact, for their own research purposes, and indepth investigation is still lack on the behavior of environmental vibration induced by freight wagons and the vibration isolation measures for freight transportation.
The research on vibration control of freight railway mainly involves attenuating the vibration in three aspects: at the source, at the receiving point, and along the transmission path. Although reinforcing the existing railway subgrade to control the vibration source is the most effective method, the normal operation of the busy railway transportation in China will be affected, and considering the organization and coordination difficulties during construction, this method is usually not used. For the reinforcement of residential buildings near the existing railway to control the vibration at the receiving point, the residents’ opinions should be sought for because their life will affect, and the construction is difficult and has high risk. Hence, it is the most feasible method to attenuate the vibration along the transmission path, and both the life of adjacent residents and the normal operation of railway transportation will not be affected.
So far, a number of scholars have studied the vibration isolation measures and methods related to vibration attenuation along the transmission path. Most of these measures can be sorted into the following types:
The first type is hollow ditch vibration isolation. Jones [7] tested the vibration isolation effect of hollow ditch along railway, and the results showed that when a ditch with depth of 35 m can bring 5 dB vibration reduction in the frequency range of 68 Hz. Ahmad and Hussaini [8] conducted a parametric study of twodimensional models of hollow ditch and filled ditch. Yang and Hung [9] conducted a similar study using the infinite element method. Adam and von Estorff [10] also numerically analyzed the isolation effects of hollow ditch and filled ditch on railway vibration. Jones [11] and Segol [12] used the finite element method, and Beskos [13], Dasgupta et al. [14], and Karlström et al. [15] used the boundary element method to study this problem. In Muenchen SolnnDeisenhofen, Germany, a slope and an empty ditch test section were built [16] and the test results showed that 515 dB vibration isolation in 1640 Hz could be achieved at the back of the ditch, but no apparent vibration isolation effect was observed in the area in a distance larger than 7 m behind the ditch.
The second type is filled ditch and vibration isolation pile wall. The vibration reduction effect of fly ash vibration isolation pile adjacent to the parallel railway near Goteborg, Sweden was studied by With et al. and it was found that the peak vibration velocity can be reduced by 4167 % in 60 m [17]. Degrande et al. [18] used this method to isolate the railway vibration at the Luxembourg station in Brussels. In addition, the vibration isolation effect of piles is numerically analyzed by Lu et al. [19]. Ekanayake, [20] also analyzed the effect of infilled, wave barriers numerically. The Belgian CDM company [21] investigated a composite vibration isolation wall with two layers of elastic material through theoretical analysis, model test and field test, and the results show salient vibration reduction effect. In recent years, the research on transmission path isolation in the European project RIVAS studied sheet pile wall by Dijckmans [22] and stiff wave barrier by Coulier [23].
The third type is the wave blocking block. In Japan, Takemiya [24] analyzed the vibration isolation effect of honeycomb block on highspeed bridge pile foundation with the case study of the impact of high speed train of Tainan Industrial Park of Taiwan on precision instruments.
The fourth type is to set large mass objects. Dijckmans [25] studied the vibration isolation effect of heavy mass in the research of transmission path isolation under the European Union project RIVAS.
The fifth type is subgrade and soil reinforcement. Thompson [26] studied the vibration isolation effect of subgrade stiffening in the research of transmission path isolation under the European Union project RIVAS.
Among these methods, hollow pitch, filled pitch and wave blocking block all require excavation over a large area between the railway and buildings, bringing hidden safety risks to the nearby railway and buildings. Hence, they are not suitable for the current situations in China, such as tight land use, and narrow space between railway and adjacent buildings. The method of vibration isolation piles is considered to be the most feasible way, which has the advantages of not being limited by the site conditions and not affecting the safety of railway and adjacent buildings.
Compared with passenger trains, freight trains have higher axle load and run at lower speed, hence larger lowfrequency vibration components are induced. The environmental vibration induced by freight trains and the vibration isolation effect of piles on vibration induced by freight rail transport were not considered in the literature mentioned above, and they have been less studied so far to our knowledge.
In this study, the environmental vibration induced by a freight train running on a typical medium to lowspeed railway in China is tested. According to the analyzed characteristics of environmental vibration, the feasibility of vibration isolation using vibration isolation piles is evaluated through simulations with a finiteelement model of the railway, stratum and building. Because slope protection piles with fixed spacing and diameter are already set up to ensure the stability of the foundation pit of the existing building and the pile spacing and pile diameter need to meet the architectural design requirements, they are not discussed in this study. Instead, the number of rows of such piles is examined, which can meet the requirements of environmental vibration isolation for medium and low speed freight rail transport.
2. Testing and evaluation of the environmental vibration caused by moving freight train
2.1. Overview of the testing conditions
The tested freight train is composed of 1 locomotive and 56 freight wagons, whose running speed is about 13.6 km/h. According to the report of stratigraphic exploration, the strata in the testing area can be divided into 11 layers, and the dynamic parameters of each soil layer are shown in Table 1. The soil elastic modulus and soil layer characteristics are obtained by field geological survey. Because the dynamic strain of soil caused by the traininduced environment vibration is in the stage of elastic deformation, a certain conversion relationship can be found between the parameters. Hence the dynamic elastic modulus and the dynamic Poisson’s ratio of soil are obtained based on the shear wave velocity and compressional wave velocity of soil measured in the geological survey. They are calculated by the following equations:
where ${c}_{p}$ and ${c}_{s}$ are the wave speeds of the $P$ wave and $S$ wave in the medium, respectively, and $\rho $ is the mass density of the medium.
Table 1. The dynamic parameters of soil layers
Stratum No.

Rock material

Density
(g/cm^{3})

Dynamic elastic modulus (MPa)

Dynamic Poisson ration

Damping ratio

Depth
(m)

1

Plain fill 1

1.890

130.6

0.33

0.05

1.5

2

Silt 2

2.010

195.1

0.33

0.05

4.2

3

Silty sand2

1.825

178.4

0.33

0.05

5.3

4

Fine sand 42

1.900

209.5

0.33

0.05

14.3

5

Silty clay 4

1.990

193.2

0.33

0.05

16.3

6

Fine sand 5

1.900

232.1

0.33

0.05

21.8

7

Silty clay 61

1.948

179.9

0.33

0.05

24.9

8

Silt 6

2.026

198.8

0.33

0.05

26.1

9

Fine sand 7

1.900

220.8

0.33

0.05

34.5

10

Silt 71

2.026

198.8

0.33

0.05

38

11

Fine sand 7

1.900

220.8

0.33

0.05

45

Two test sections perpendicular to the moving direction of the train are set up on the spot near the railway side. Test section A is located on the east side of the 3# building, and Test section B is located on the east side of the 1# building. In each section, four measuring points are located, and the time history data of the vertical acceleration is collected at each measuring point. A sketch map of the test sections and measuring points is shown in Fig. 1 and the detailed information about the location of each measuring point is listed in Table 2.
Fig. 1. Diagram of the test sections
2.2. Evaluation criterion
According to the existing “Urban regional environmental vibration standards” (GB1007088) for railway, the weighted vibration acceleration level as a function of time $t$ in the vertical direction (i.e. $VLz$ in the following section) in the residential area and the cultural and educational area should not be higher than 70 dB and 67 dB during the day and at night, respectively; in the region 30 m and larger away from the central line of the outer track, the $VLz$ should not be higher than 80 dB. Therefore, field measurement is conducted at sensitive locations within 0.5 m away from the outer wall of buildings in an adjacent residential area and at a site 30 m away from the central line of the outer track.
Table 2. Arrangement of measuring points
Test section

Measuring point

Distance away from the track central line/m

Measured item

A

Point A1

29

Environmental vibration adjacent to the railway

Point A2

32

Environmental vibration before the slope protection piles


Point A3

34.1

Environmental vibration before the slope protection piles


Point A4

43

Environmental vibration outside residential buildings


B

Point B1

9

Environmental vibration adjacent to the railway

Point B2

34.1

Environmental vibration before the slope protection piles


Point B3

39.9

Environmental vibration before the slope protection piles


Point B4

46

Environmental vibration outside residential buildings

2.3. Test results and discussions
In this section, the data collected when a fully loaded freight train is passing by is taken as the typical data for analyzing the characteristics of the induced soil vibration. The time history and frequency analysis of the recorded data are carried out.
Fig. 2 and 3 show the time histories of the acceleration signals recorded at the measuring points in Section A and B, respectively. The plots demonstrate small difference between the acceleration signals collected at different measuring points in Section A and B. The maximum acceleration is not more than 0.002 g, and the amplitude of acceleration decreases more significantly when the vibration is transmitted to Measuring point A4 or B4.
Fig. 2. Acceleration signals recorded in test section A
a) Measuring point A1
b) Measuring point A4
Fig. 3. Acceleration signals recorded in test section B
a) Measuring point B1
b) Measuring point B4
Fig. 4 and 5 show the time history curves of the weighed vibration acceleration level as a function of time $t$ in the vertical direction ($VLz$) at different measuring points in the two test sections, and $VLz$ is expressed as:
where ${a}_{0}$ is the reference acceleration, defined to be 10^{6} m/s^{2}, and ${a}_{w,\tau}\left(t\right)$ is the running r.m.s. of the weighted acceleration, which is expressed as:
The plots indicate that when the freight train is passing by, the $VLz$ is distributed in the range of 5077 dB in Section A, and in the range of 4574 dB in Section B; moreover, with the increase of distance between the measuring point and the railway, the maximum values of $VLz$ on both test sections gradually decrease. In Section A, at the measuring points 29 m and 43 m away from the central line of the railway, the maximum values of $VLz$ are 77 dB and 75 dB, respectively. In Section B, the maximum values of $VLz$ are 74 dB and 71 dB at the measuring points 29 m and 46 m away from the central line of the railway, respectively.
Table 3 lists the calculated maximum $VLz$ based on the data recorded at all measuring points in Section B. In the region adjacent to the railway, the $VLz$ is lower than 80 dB during the day and at night, so the requirement in the standard is satisfied. However, in the region 0.5 m away from the outer wall of buildings in the residential area, the $VLz$ is in the range of 5874 dB, which is 04 dB higher than the specified limit during the day and 02 dB higher than the specified limit at night. Hence the environmental vibration in the residential area cannot meet the requirement in the standard, and vibration isolation measures must be adopted.
Fig. 4. The measured $VLz$ at each test point located in section A
Fig. 5. The measured $VLz$ at each test point located in section B
Table 3. The $VLz$ measured in test section B
Measuring point

Time

$VLz$ (dB)

Vibration level above the requirement (dB)

B1

Daytime

69.91

Satisfactory

B4

Daytime

71.97

1.97

B1

Daytime

76.13

Satisfactory

B4

Daytime

73.76

3.76

B1

Night

68.37

Satisfactory

B4

Night

57.60

Satisfactory

B1

Night

69.31

Satisfactory

B4

Night

68.94

1.94

In order to further analyze the spectral characteristics of the environmental vibration induced by freight train, the 1/3octave spectra of $VLz\left({f}_{i}\right)$ at the four measuring points in each test section when the train is passing by are presented in Fig. 6 and 7. $VLz$$\left({f}_{i}\right)$ is defined as the weighted vibration acceleration level as a function of the central frequency ${f}_{i}$ in the vertical direction, and is expressed as:
where ${a}_{0}$ is the reference acceleration, defined to be 10^{6} m/s^{2}, and ${a}_{w}\left({f}_{i}\right)$ is the weighted acceleration level as a function of the central frequencies in the onethird octave bands. It can be known that for Section A, the fundamental frequency is between 412Hz and the vibration level is distributed in the range of 6575 dB; for Section B, the fundamental frequency is between 815 Hz, and the vibration level is distributed in 6575 dB. At all the four measuring points in the same test section, the fundamental frequencies are very close, and at all the measuring points in both sections, the vibration level declines significantly at frequencies above 20 Hz.
Fig. 6. The 1/3octave spectrum of the measured $VLz\left({f}_{i}\right)$ at each test point located in section A
Fig. 7. The 1/3octave spectrum of the measured $VLz\left({f}_{i}\right)$ at each test point located in section B
3. Theoretical model
In order to examine the vibration isolation effect of different arrangements of piles in row, a “vehicletrack” model and a finiteelement “railwaystratumbuilding” model is constructed. The fastener force derived with the vehicletrack model is taken as the excitation source and applied to the railwaystratumbuilding model, and then the vibration acceleration response of the soil is obtained for different arrangements of vibration isolation piles. By analyzing the calculated results, the final arrangement of vibration isolation piles is determined, which meets the requirements of vibration control in the planned building area.
3.1. The dynamic model of the vehicle and track
In order to accurately simulate the contact force between the vehicle wheel type and track (force of fastener), the C64 freight wagon commonly used in practice is considered as the vehicle in the model, and the diagram of the axle loads is shown in Fig. 9. According to the actual situation, the vehicle model has reasonably simplified structure and assumptions are made to ensure the validity of simulation results to the maximum extent.
3.1.1. Vehicle model
A simplified model of the vehicle is shown in Fig. 8. Considering the nodding and updown movements of the vehicle body and bogie, the model has a total of six degrees of freedom, and the equations of motion for each component of the vehicle are listed in Eqs. (4)(13).
Fig. 8. The vehicle model
Updown movement of car body:
Nodding motion of car body:
where ${z}_{c}$ is the vertical displacement of car body; ${\phi}_{c}$ is the rotational displacement of car body; ${z}_{t1}$ and ${z}_{t2}$ are the vertical displacement of the front bogie and rear bogie, respectively; ${m}_{c}$ is the mass of the car body; ${J}_{c}$ is the moment of inertia of the car body; ${k}_{sz}$ and ${c}_{sz}$ are the spring stiffness and damping coefficient of the second suspension system; ${l}_{c}$ is half of the longitudinal distance between the centers of gravity of the front bogie and the rear bogie.
Updown movement of front bogie:
Nodding motion of front bogie:
Updown movement of rear bogie:
Nodding motion of rear bogie:
where ${\phi}_{t1}$ and ${\phi}_{t2}$ are the rotational displacements of the front bogie and rear bogie, respectively; ${z}_{w1}$, ${z}_{w2}$, ${z}_{w3}$ and ${z}_{w4}$ are the vertical displacements of the four wheel sets; ${m}_{t}$ is the mass of bogie frame ; ${J}_{t}$ is the moment of inertia of the bogie frame; ${k}_{pz}$ and ${c}_{pz}$ are the spring stiffness and damping coefficient of the primary suspension system, respectively.
Updown movement of the 1st wheelset:
Updown movement of the 2nd wheelset:
Updown movement of the 3rd wheelset:
Updown movement of the 4th wheelset:
where ${z}_{w1}$, ${z}_{w2}$, ${z}_{w3}$, and ${z}_{w4}$ are the vertical displacements of the four wheel sets; ${m}_{w}$ is the mass of the wheelset;
The vehicle is considered in accordance with the C64 freight train, and the layout of the train load is shown in Fig. 9.
Fig. 9. Diagram of the axle loads of the C64 freight wagon
3.1.2. Track model
The model of the track is obtained using the finite element method, and it is written as:
where:
where $NE$ denotes the number of elements; $\alpha $ and $\beta $ are the Rayleigh damping coefficients; $nw$ is number of wheelset.
${q}_{i}^{e}$ is the displacement vector of the $i$th element node, and can be written as:
where ${y}_{2i1}$ and ${y}_{2i+1}$ are the vertical deflections of the (2$i$)th and (2$i$+2)th element node, respectively; ${\phi}_{2i}$,${\phi}_{2i+2}$are the rotational angle of the (2$i$)th^{}and (2$i$+2)th^{}element node, respectively.
${m}_{rail}^{e}$ is the mass matrix of rail element, and may be expressed as:
where $l$ is the element length, and ${m}_{r}$ is the mass per unit length of rail.
${k}_{rail}^{e}$ is the stiffness matrix of rail element, and can be written as:
where $E$ is the bending stiffness of the rail, and $I$ is the bending moment of inertia of the rail.
${k}_{spring}^{e}$ is the stiffness matrix of the support element, and can be written as:
where ${k}_{s}$ is the stiffness coefficient of the fastener.
${Q}_{p}^{e}$ _{}is the vector of loads acting on the rail, and can be written as:
where ${P}_{wi}$ is the force between wheel and rail, and $N$ is the Hermitian cubic interpolation function.
Since each wheel is assumed to be always in contact with the rail beam, the force between rail and wheel can be expressed as:
$+{m}_{w}{\ddot{z}}_{wi}+{m}_{w}g.$
When “$i=$ 1, 2”, $j=$ 1; when “$i=$ 3, 4”, $j=$ 2.
The vertical displacements of the wheel sets ${Z}_{wi}$ are calculated by the vertical deflections of rail and rail irregularities ${r}_{i}\left(t\right)$, and can be expressed as:
In this paper, the trigonometric series method is used to simulate the power spectrum density function in the presence of track irregularity on the Shuohuang Railway in China, and the timedomain sample of track irregularity is shown in Fig. 10.
Fig. 10. Track irregularity
In order to save the computing time, a group of three wagons is considered, running at the speed of 13.6 km/h. The step size of integration is 0.05 s, and the cutoff frequency is 100 Hz in the computation, meeting the requirements in calculating the response of ground surface velocity. The force acting on the fastener is calculated by:
The calculated time history of the force acting on the fastener is shown in Fig. 11.
3.2. The finiteelement model of the trackstratumbuilding system
3.2.1. Structure description
This paper focuses on the residential buildings which are close to the existing medium to lowspeed freight railway lines, and vibration attenuation measures cannot be applied to them nor the vibration source because of the limitations imposed by the site conditions. The feasibility of modifying the slope protection piles outside the building to make them function as vibration isolating piles is explored in this study. Such modification on the slope protection piles makes them not only play the role of building foundation pit protection but also have vibration isolation effect.
The research in this paper is based on the actual engineering background, and the specific project is shown in Fig. 12. Outside the building, a row of slope protection piles have already been set up to ensure the stability of foundation pit excavation. According to the requirements of building construction, the diameter of each pile is 600 mm, and the spacing between piles is 1200 mm. For this project, we proposed a double row pile vibration isolation scheme by adding another row of similar piles on the outside of the existing pile row.
Fig. 11. The derived force of fastener
Fig. 12. The arrangement of double row vibration isolation piles
3.2.2. Track model
In order to accurately simulate the environmental vibration induced by the freight train, a model of nonballasted slab track is constructed using the C3D8R solid elements in the finite element analysis software ABAQUS. The sizes and the material properties of the track slab and base plate are shown in Table 4 and 5, respectively. The structure of the track is shown in Fig. 12.
Table 4. Size of the track
Parts

Length (mm)

Height (mm)

Width (mm)

Track slab

46000

200

2400

Base plate

46000

300

3000

Table 5. Track material properties
Parts

Elastic modulus (N/m^{2})

Poisson ratio

Density (kg/m^{3})

Track slab

3.60e10

0.167

2500

Base plate

3.25e10

0.167

2500

3.2.3. Building model
The building model takes the 2# and 3# residential building in the Shangchenghuadu residential area as the prototype; the ground part has 14 stories and the underground part has 2 stories, with a total of 16 stories. The finite element model is constructed with the S4 shell element in ABAQUS, and the element thickness is 0.3 m, as shown in Fig. 13.
Fig. 13. The track model
3.2.4. Stratumpile model
A stratum model is constructed under three conditions: with no piles, with a single row of piles and with double rows of piles, to analyze the vibration isolation effect of different schemes of pile arrangement (the details are shown in Table 6). According to the shear wave velocity of the soil stratum and the size requirement in a dynamic finite element model, the size of the stratum model is determined to be “100 m×50 m×50 m”, In addition, the soil strain induced by rail transport is generally less than 10^{5}, and at this point the soil is in the elastic state [14], so the soil is assumed to be linear elastic constitutive in this model. The soil model is divided into 11 layers according to the survey result on site.
The dynamic parameters of each layer are shown in Table 1. The piles and soil stratum are simulated with the C3D8R solid elements, and the surface binding relationship is defined between the piles and soil, so relative sliding is not allowed to occur and the actual force applied to the piles can be simulated. In order to prevent the reflection of waves on the manually defined stratum boundaries, a layer of soil mass extending in five infinite directions is defined to simulate an infinitely large stratum, which is constituted by the CIN3D8 infinite elements. Based on the definitions mentioned above, the case with piles in double rows is shown in Fig. 14, as an example of the constructed trackstratumbuilding model.
Fig. 14. The overall stratumpile model
a) Whole model
b) Cross section wireframe
Table 6. Parameters of row piles
Computed cases

No. of rows

Pile diameter (mm)

Interpile spacing (mm)

1

0

–

–

2

1

600

1200

3

2

600

1200

3.3. Model validation
The model is validated based on the test data in Section A. Fig. 15(a) and (b) show the simulated and measured acceleration signal of soil mass vibration, respectively, and the measured and simulated maximum $VLz$ at locations with different distances away from the railway are listed in Table 7. The elastic modulus of the surface soil in the finite element model is adjusted by comparing the time history of the acceleration calculated with the model to that of the measured acceleration. The figures show that the simulated and measured amplitudes of the acceleration signals of soil mass vibration are consistent on the order of magnitude, and both have the maximum acceleration not more than 0.0015 g. The table shows that when the train is passing by, the simulated and measured maximum $VLz$ are both around 75 dB. Therefore, the measured and simulated results are generally in good agreement, and the finite element model constructed in this paper is validated.
Fig. 15. Vertical acceleration of the soil mass 28.8 m away from the track central line
a) Simulated result
b) Measured result
Table 7. The simulated and measured maximum $VLz$
Measuring point

Measured result (dB)

Simulated result (dB)

A1

74.8

73.1

A2

75.2

73.7

A3

74.8

74.3

A4

74.2

72.1

4. Vibration isolation effect of piles in row
Based on the finite element model constructed above, the environmental vibration induced by the freight train running at 13.6 km/h is simulated for different pile arrangements, and the time history of acceleration at the key positions is obtained. Then the vibration isolation effects of different pile arrangements are analyzed.
Fig. 16 shows the vibration isolation effect of different pile arrangements. It can be known that in the absence of piles, the propagation of ground vibration caused by the running freight wagon is only blocked by the building. After the piles are set up, it can be clearly seen that the transmission of ground vibration is blocked by the piles. In addition, the effects of different pile arrangements on vibration isolation can be directly seen, i.e. the more number of rows are the piles placed in, the better the vibration isolation effect is.
The vibration isolation effects of different pile arrangements are further demonstrated by the vibration of soil mass in front of and behind the piles. Fig.17 and 18 show the time history of acceleration before and after different pile setups, respectively. It is shown that the piles have significant vibration isolation effect in front of and behind the piles. The piles in double rows reduces the soil mass vibration acceleration in front of piles by 55 % compared with the piles in a single row, and the soil vibration acceleration in front of a single row of piles is decreased by 33 % compared with that in the absence of piles. Behind the piles in double rows, the soil mass vibration acceleration is reduced by 25 % compared with that behind the piles in a single row, and the soil vibration acceleration behind a single row of piles is decreased by 30 % compared with that in the absence of piles. In general, for both pile arrangements, the levels of vibration acceleration behind piles are all lower than those in front of piles, according with the law of vibration attenuation. Moreover, the doublerows setup has better effects of soil vibration reduction than the singlerow setup.
Fig. 16. Colored maps displaying the vibration isolation effects of different arrangements of piles
a) With no piles
b) With piles in one row
c) With piles in two rows
Regarding the spectral characteristics of vibration, Fig. 19 and 20 show the 1/3octave spectra of the weighted vibration acceleration level as a function of time central frequency ${f}_{i}$ in the vertical direction ($VLz\left({f}_{i}\right)$) in front of and behind different pile arrangements, respectively, when the freight train is passing by. For different pile arrangements, the fundamental frequency of ground vibration in front of and behind piles is in the range of 425 Hz, and the $VLz$ is distributed in 5570 dB. Compared with the case without piles, 05 dB reduction of the $VLz$ is achieved in front of the piles in a single row, and 09dB reduction is achieved in front of the piles in double rows. In the lowfrequency range (below 10 Hz), compared with the case without piles, 24 dB reduction of the $VLz$ is achieved behind the piles in a single row, and 210 dB reduction in the lowfrequency range is achieved behind the piles in double rows. Therefore, with the increase of the number of pile rows, the $VLz$ shows a decreasing trend. It can be seen that vibration isolation piles can reduce the $VLz$ to some extent both in front of and behind the piles.
In order to analyze the attenuation of the maximum vibration level in the $Z$ direction with distance, the weighed vibration acceleration level as a function of time $t$ in the vertical direction ($VLz$) at different locations away from the track center line are shown in Fig. 21, for different arrangements of piles. Compared with the case without piles, the $VLz$ can be reduced by 24 dB with the singlerow setup, and can be reduced by 410 dB with the doublerow setup.
Field test results show that within 0.5 m outside a building in the residential area, the $VLz$ is 04 dB higher than the specified limit during the day and 02 dB higher than the limit at night. Hence, the isolation scheme using doublerow piles can satisfy the specified limits.
Fig. 17. The time histories of the acceleration signals in front of piles
Fig. 18. The time histories of the acceleration signals behind piles
Fig. 19. The 1/3octave spectra of the $VLz\left({f}_{i}\right)$ in front of piles
Fig. 20. The 1/3octave spectra of the $VLz\left({f}_{i}\right)$ behind piles
Fig. 21. Variation of $VLz$ with the distance from the track central line
5. Conclusions
The test result of environmental vibration induced by a medium to low speed running freight train shows that in the region adjacent to the railway, the weighed vibration acceleration level as a function of time $t$ in the vertical direction ($VLz$) is lower than 80 dB, which meets the requirements of the “Urban regional environmental vibration standards” (GB1007088) for railway; however, in the surrounding residential area, the $VLz$ is in the range of 5874 dB, which is 04 dB higher than the specified limit during the day and 02 dB higher than the specified limit at night.
For the isolation of environmental vibration induced by this medium to low speed running freight train, the vibration isolation effect of building slope pit protection piles is simulated by constructing a “vehicletrack” model and a finiteelement model of the railway, stratum and building, and the result shows that the doublerow setup of piles can attenuate the environmental vibration in the residential area to levels satisfying the same standard: the $VLz$ can be reduced by 410 dB within 5 m behind the piles in double rows. Hence the doublerow setup is recommended for the isolation of environmental vibration induced by medium to low speed freight rail transport under similar conditions.
The simulated results demonstrate the vibration isolation effects of different pile rows. The piles in double rows reduces the soil mass vibration acceleration in front of piles by 55 % compared with the piles in a single row, and the soil vibration acceleration in front of a single row of piles is decreased by 33 % compared with that in the absence of piles. Behind the piles in double rows, the soil mass vibration acceleration is reduced by 25 % compared with that behind the piles in a single row, and the soil vibration acceleration behind a single row of piles is decreased by 30 % compared with that in the absence of piles.
Compared with the case without piles, 05 dB reduction of the $VLz$ is achieved in front of the piles in a single row, and 09 dB reduction is achieved in front of the piles in double rows. In the lowfrequency range (below 10 Hz), compared with the case without piles, 24 dB reduction of the $VLz$ is achieved behind the piles in a single row, and 210 dB reduction in the lowfrequency range is achieved behind the piles in double rows.
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Cited By
Sustainability
Meng Ma, Bolong Jiang, Weifeng Liu, Kuokuo Liu

2020
