Effects on some clay soil qualities following the passage of rubber-tracked and wheeled tractors in...
Transcript of Effects on some clay soil qualities following the passage of rubber-tracked and wheeled tractors in...
Effects on some clay soil qualities following the passage ofrubber-tracked and wheeled tractors in central Italy
P. Servadioa,*, A. Marsilia, M. Pagliaib, S. Pellegrinib, N. Vignozzib
aAgricultural Mechanization Research Institute, Via della Pascolare, 16, Monterotondo, Rome, ItalybResearch Institute for Soil Study and Conservation, Piazza D’Azeglio 30 50121 Florence, Italy
Received 28 January 2000; received in revised form 29 January 2001; accepted 22 February 2001
Abstract
There is increased use of rubber-tracked tractors for ploughing on clay soil (Vertic Cambisol) in central, south and insular
Italy instead of metal-tracked tractors, because they allow travel on public roads. Field tests were carried out on arable soil
previously ploughed and harrowed to compare two types of tractors, one rubber-tracked (CAT Challenger Ch 45) and one
wheeled (New Holland 8770) in order to establish the compacting effects resulting from 1 and 4 passes of the tractors in the
same track. The following parameters were studied: soil penetration resistance, bulk density and its increment ratio, soil shear
strength, soil macroporosity and hydraulic conductivity. Multiple passes made by the two tractors induced very similar effects
on the soil in regards to soil penetration resistance. Mean values of penetration resistance (0–0.20 m depth) were 1.15 MPa for
the rubber-tracked tractor and 1.11 MPa for the wheeled tractor; mean values of penetration resistance (0.21–0.40 m depth)
were 1.07 MPa for the rubber-tracked tractor and 1.17 MPa for the wheeled tractor. The decrease in macroporosity, in
particular that of elongated pores in the soil surface layer (0–0.10 m depth) was greater in treatments involving the rubber-
tracked tractor (from 20.2 to 2.7%) than for the wheeled tractor (from 20.2 to 10.3%). Following traffic of the two tractors,
hydraulic conductivity decreased and the following values were found for the five treatments: control, 18.48 mm h�1; wheeled
tractor 1 and 4 passes, 11.15 and 7.45 mm h�1, respectively; rubber-tracked tractor 1 and 4 passes, 3.25 and 1.1 mm h�1,
respectively. Highly significant correlations between shear strength and dry bulk density, and between hydraulic conductivity
and elongated pores and total macroporosity were found. Significant linear relationships between macroporosity and
penetration resistance for 1 and 4 passes of both tractors were found in the soil layers (0–0.10 m). A significant difference was
found between tractors and for correlations of penetration resistance values above control values. However, in the soil layer
(0–0.20 m depth), with respect to the higher degree of macroporosity and low values of penetration resistance, treatments
involving wheeled tractor (1 pass) showed a lower degree of soil compaction than was observed after 1 pass of the rubber-
tracked tractor. # 2001 Elsevier Science B.V. All rights reserved.
Keywords: Rubber-tracked tractor; Wheeled tractor; Soil compaction; Soil porosity; Soil penetration resistance; Soil shear strength; Soil
structure; Central Italy
1. Introduction
Metal track-type tractors have the potential for
causing less soil compaction than wheeled tractors
because the tracks usually have a greater surface
area than wheels for tractors with equivalent power
Soil & Tillage Research 61 (2001) 143–155
* Corresponding author. Tel.: þ39-6-906-7917;
fax: þ39-6-906-25591.
E-mail address: [email protected] (P. Servadio).
0167-1987/01/$ – see front matter # 2001 Elsevier Science B.V. All rights reserved.
PII: S 0 1 6 7 - 1 9 8 7 ( 0 1 ) 0 0 1 9 5 - 7
ratings (Brown et al., 1992) and they are used in
many farming areas where large drawbar loads are
required. Other advantages include the large ground
contact area of the track resulting in high tractive
efficiencies, high dynamic traction ratios, low ground
pressures and good stability on steep slopes (Sofiyan
and Maximenko, 1965; Rowland, 1972; Brusentsev,
1967).
In two previous studies (Marsili and Servadio,
1996; Marsili et al., 1998), compaction of clay soil
was investigated after the passage of rubber and metal-
tracked tractors. The first study was carried out on
tractors with medium power of 52 kW (rubber tracks)
and 55 kW (metal tracks), and the second study was
carried out on high power tractors of 131 kW (rubber
tracks) and 114 kW (metal tracks). Both tests indi-
cated that metal tracks cause less compaction than
rubber tracks in agreement with Bekker (1969). The
lower compaction caused by metal tracks was attrib-
uted to the more uniform stress distribution on the soil
compared to the rubber track, and this advantage
resulted in a significantly lower bulk density and
penetration resistance in the uppermost soil layers
for a higher number of tractor passes. In the second
test, where soil structure measurements were intro-
duced, it emerged that with respect to the higher
degree of macroporosity, treatments involving the
metal-tracked tractor showed better soil structure
quality than did the rubber-tracked tractor. However,
rubber-tracked tractors have the advantage of being
able to run on concrete and other road surfaces, and
can be made lighter than metal-tracked tractors of
equivalent performance. In this paper, further studies
were carried out using a rubber-tracked tractor in
comparison with a wheeled tractor. Although there
is an almost universal use of wheeled tractors in Italy,
rubber-tracked tractors are now used on clay and
steeply sloped soil, particularly in south, central and
insular areas, in preference to metal-tracked tractors,
because they combine high tractive efficiencies, high
dynamic traction ratios and low soil compaction
attributes of tracked tractors with the high travel speed
and manoeuvrability of 4-wheel drive tractors (Esch
et al., 1990), and they are allowed to travel on public
roads.
Increased awareness of soil conservation problems
has stimulated interest in soil dynamics studies (Scha-
fer and Johnson, 1990) and in soil compaction. Studies
on soil compaction in recent years have included:
laboratory simulation (Koolen, 1974; Burt et al.,
1980; Willatt, 1987; Dawidowski and Lerink,
1990), prediction or statistical correlation between
many of the relevant properties (Ahuja et al., 1984;
Koolen and Vaandrager, 1984; Ohu et al., 1986), and
field experiments (Verma et al., 1976; Greenland,
1977; Raghavan et al., 1978; Russell, 1978; Way
et al., 1995; Wiermann et al., 1999). Other studies
have included field experiments on compaction in
relation to crop production (O’Sullivan, 1992; Lowery
and Schuler, 1994; Soane and Van Ouwerkerk,
1994a,b, 1995; Arvidsson and Hakansson, 1996). In
most of these studies, changes to soil physical proper-
ties following externally applied loads were studied,
but continuous technological progress of the agricul-
tural machines with respect to running gear, axle
loads, etc. have necessitated new field tests and studies
in order to evaluate the significance of mechanical
compaction to soil use and, eventually, to optimize soil
management.
Soil properties which are pertinent to agricultural
soil use, and which are affected during field opera-
tions, are referred to as soil qualities (Koolen, 1987).
Soil qualities was introduced as a generic term for soil
physical and mechanical properties which are relevant
for soil use, and include workability, trafficability,
water and air conductivities, water and air storage
capacities, thermal and strength properties, erodibility,
stability, and root penetrability. Soil physical and
mechanical properties are generally dependent also
on the soil moisture content (Dawidowski and Lerink,
1990).
In this study, measurements were made on the
effects on some clay soil qualities following the
passage of two tractors, one equipped with a rubber
belt track design and one with tires. The primary
objective of this study was to investigate compac-
tion of a ploughed and harrowed clay soil subjected
to successive tractor passes. Parameters measured
included soil penetration resistance, bulk density
and its increment ratio, soil shear strength, soil
porosity and hydraulic conductivity. The second
objective was to develop statistical correlations for
the soil layers tested between soil penetration resis-
tance and porosity, between soil porosity and hydrau-
lic conductivity and between bulk density and soil
shear strength.
144 P. Servadio et al. / Soil & Tillage Research 61 (2001) 143–155
2. Materials and methods
2.1. Soil and treatments
The field tests were carried out using two large trac-
tors, fitted with different types of running gear, one with
rubber tracks (CAT Challenger 45) and the other with
four drive wheels (New Holland 8770). The main
technical characteristics of these tractors and their run-
ning gear are given in Tables 1 and 2. On a plain terrain
30 km north of Rome, compaction tests were carried out
on a well drained clay soil, classified as Vertic Cambisol
(FAO, 1988). The soil was previously ploughed to
0.40 m depth in March and harrowed to 0.20 m depth
with rotary harrow in April 1999. Two months after
harrowing, tractor passes were applied to the soil, 1 and
4 passes on the same track left by the tractor for a total of
four treatments, in a randomised block of eight plots,
each 420 m2. Measurements were also made on a con-
trol area with no traffic adjacent to every plot (Table 3).
Forward speed was 0.50 m s�1 for both tractors.
The initial soil conditions are given in Table 4. Soil
moisture content was measured at a depth from 0 to
0.20 m by taking samples of soil immediately outside
the track left by the tractors and in the control areas
using a corer sampling ring. These samples were
weighed and dried until they reached a constant
weight. Soil compaction was quantified by measuring
cone penetration resistance, dry bulk density, and
shear strength and soil structure was determined by
measuring porosity and hydraulic conductivity.
2.2. Penetration resistance and dry bulk density
Soil penetration resistance was measured in the
tracks left by each tractor after 1 and 4 passes and
Table 1
Main technical characteristics of the rubber-tracked tractor and its track used in the traffic studies
Characteristics CLAAS-CAT Ch 45 tractor
Measured mass with ballast (kg) 11895
PTO power (kW) 179
Track tread (m) 1.895
Overall width (m) 2.525a
Overall length (m) 5.40
Cabin height max (m) 3.5
Height above soil of implement hitch (m) 0.48
Type of track Two reinforced rubber tracks
Total track length (m) 8.60 external
Track thickness (m) 0.028
Lugs per track (number) 36 � 2
Distance between centres of lugs (m) 0.24
Lug height (m) 0.063
Lug width (m) 0.30
Radius of steering area (m) 2.80
Supporting wheels (number) 3b
Diameter of driving wheel (m) 1.455
Diameter of support wheels (m) 0.36
Diameter of track wheel (m) 0.80
Theoretical ground contact length (m) 2.20
Track width (m) 0.635
Total area of support of the two tracks on firm soil (m2) 1.61c
Average ground contact pressure (kPa) 72.5
Track pre-tension load (kN) 59
a Version used for the tests.b Drive wheels not included.c Total area of support of the two tracks on firm soil (Ta) was estimated as follows: Ta ¼ 0:3ðEddw þ Edtw þ 3EdswÞ � Tw � 2, where
Eddw is the external diameter of driving wheel; Edtw the external diameter of track wheel; Edsw the external diameter of support wheels; Tw
the track width (external diameter is diameter of wheel þ two tracks and lugs thickness).
P. Servadio et al. / Soil & Tillage Research 61 (2001) 143–155 145
on the control areas, which had no traffic, using an
Eijkelkamp penetrologger (electronic penetrometer)
with a 608 cone and base area of 100 mm2 driven into
the soil at a constant rate (5 cm s�1). For each plot,
including the control areas, 20 penetrometer readings
were taken in increments of 1 cm at depths of 0–
0.40 m. Dry bulk density was measured by taking
samples of soil below the tracks left by each tractor,
Table 2
Main technical characteristics of the wheeled tractor and its tires used in the traffic studies
Characteristics New Holland 8770 tractor
Measured mass with ballast (kg) 10128
PTO power (kW) 140
Wheel tread (m) 1.780
Overall width (m) 2.500
Overall length (m) 4.970
Cabin height max (m) 3.070
Height above soil of implement hitch (m) 0.500
Type of tires Front Good Year Rear Good Year
Identification initials DT 820 600/65 R28 DT 820 710/70 R38
Open centre Yes Yes
Wheel rim DW 20 A DW 23 A
Rim diameter (m) 0.711 0.965
Section of tire (maximum width) (m) 0.622 0.715
Aspect ratio (height/width) 0.650 0.700
Rolling radius (m) 0.670 0.855
External diameter (m) 1.491 1.932
Lugs number (number) 38 38
Lugs height (m) 0.047 0.053
Lugs width (m) 0.043 0.060
Lugs angle (8) 45 40–45
Load on the two tires (kN) 45.57 55.70
Total contact area of the two tires on firm soil (m2) 0.56a 0.83a
Theoretical ground contact pressure (kPa) 70.9 71.8
Inflation pressure (kPa) 140 160
a Total contact area of the two tires on firm soil (Ta) was estimated as follows: Ta ¼ St � 0:3 � Ed � 2, where St is the section of the tire;
Ed the external diameter.
Table 3
Treatments determined by type of tractor and number of passes
Treatments Type of tractor Number of passes
on same track
RT-1 Rubber-tracked 1
RT-4 Rubber-tracked 4
WT-1 Wheeled 1
WT-4 Wheeled 4
Control No passes
Table 4
Soil physical properties of the Vertic Cambisol used in the traffic
studies
Property g kg�1
Soil organic carbona (0–0.50 m depth) 19
Particle size distributionb
Sand (2000–50 mm) 120
Silt (50–2 mm) 320
Clay (<2 mm) 560
Plastic limitc 265
Liquid limitc 525
Plastic indexc 260
Moisture content
At depth of 0–0.10 m 300
At depth of 0.11–0.20 m 350
a Determined by Walkley and Black (1934).b Determined by hydrometer method (Cestelli Guidi, 1987).c Determined by Atterberg limits (Cestelli Guidi, 1987).
146 P. Servadio et al. / Soil & Tillage Research 61 (2001) 143–155
after 1 and 4 passes and from the control areas using a
corer with a 100 cm3 volume sample ring (internal
diameter 5 cm, length 5.1 cm and wall thickness of
0.15 cm) at depths of 0–0.05, 0.06–0.10, 0.11–0.15
and 0.16–0.20 m. These samples were weighed and
dried until they reached a constant weight. In addition,
the increment ratio of density (Gn) was used as a
compaction criterion (Fujii, 1992) and is defined as
Gn ¼ gn � g0
g0
¼ gn
g0
� ��1
(1)
where g0 is the initial density (control) and gn the
density after the nth (1 and 4) tractor passes.
2.3. Shear strength measurement
Soil shear strength, as a parameter to measure
vehicle–soil interaction (Wong, 1993), was measured
in the tracks left by each tractor after 1 and 4 passes
and on the control areas, which had no traffic, using a
Stahlwille Manoskop vane shear test meter with a
torsion wrench from 8 to 32 Nm, vane diameter
70 mm and vane height 30 mm driven into the soil
at a constant rate. For each plot, including the control
areas, six measures were taken at 35 mm increments
within depths of 0–0.35 m. Shear resistance (t)
(N m�2) was calculated with the Terzaghi and Peck
(1979) relationship to applied torque.
2.4. Macroporosity and saturated hydraulic
conductivity measurements
The pore system was characterized by image ana-
lysis on thin sections from undisturbed soil samples.
For this, six undisturbed samples were collected in the
surface layer (0–0.10 m) and in the 0.10–0.20 m layer
of control plots and in the areas compacted by 1 and 4
passes of each tractor.
Samples were dried by acetone replacement of
water (Murphy, 1986), impregnated with a polyester
resin and cut into 6 cm � 7 cm, vertically orientated
thin sections (Murphy, 1986). Such sections were
analysed by means of image analysis techniques
(Pagliai et al., 1984), using the IMAGE PRO-PLUS
software produced by Media Cybernetics (Silver
Spring — USA). The analysed image covered
4:5 � 5:5 cm2 of the thin section, avoiding the edges
where disruption can occur. Total porosity and pore
distribution were measured according to their shape
and size. In this experiment, the instrument was set up
to measure pores larger than 50 mm (macroporosity).
Pores were measured by their shape, which is
expressed by the shape factor (perimeter2/(4p�area))
and divided into regular (more or less rounded) pores
(shape factor 1–2), irregular pores (shape factor 2–5)
and elongated pores (shape factor >5). These classes
correspond approximately to those used by Bouma
et al. (1977). Pores of each shape group were further
subdivided into size classes according to either the
equivalent pore diameter for regular and irregular
pores, or the width for elongated pores (Pagliai
et al., 1983, 1984). Thin sections were also examined
using a Zeiss ‘‘R POL’’ microscope at 25� magnifica-
tion to observe soil structure.
To measure saturated hydraulic conductivity, six
cores (5.68 cm diameter and 9.5 cm high) were col-
lected from the 0 to 0.10 m layer of each plot in areas
adjacent to those sampled for thin section preparation.
The samples were slowly saturated and saturated
hydraulic conductivity was measured using the fall-
ing-head technique (Klute and Dirksen, 1985).
3. Results and discussion
3.1. Penetration resistance and dry bulk density
Mean values of soil penetration resistance at various
depths (from 0 to 0.40 m in increments of 0.05 m),
standard deviations of the mean and coefficients of
variation for the various plots are shown in Table 5,
subdivided by tractor type (RT and WT) and number
of passes of the same track (1 and 4) in addition to
those for the control plots. Table 6 shows dry bulk
densities and the increment ratio of density (Gn) after 1
and 4 passes on the same track left by the tractors.
Results shown in Tables 5 and 6 indicated that for both
tractors, soil penetration resistance and dry bulk den-
sity increased with the number of passes on the same
track and this finding agrees with that of other studies
(Marsili and Servadio, 1992, 1996; Marsili et al.,
1998).
Examining the values of penetration resistance for
different soil layers (Table 5) and comparing the RT-1
and RT-4 passes with the control plot, it appears that
differences were statistically significant only in the
P. Servadio et al. / Soil & Tillage Research 61 (2001) 143–155 147
upper layers (0–0.15 m depth), while differences
between WT-1 and WT-4 passes and the control plot
were statistically significant only in the upper two
layers (0–0.10 m depth).
A comparison of the mean penetration resistance
for 1 pass of the two tractors shows that in the layers
there was a statistically significant difference between
the RT-1 pass and WT-1 pass in favour of the WT-1
pass only in the upper layers (0–0.15 m depth), while
in the deeper layers (0.26–0.40 m) there was a statis-
tically significant difference between WT-1 pass and
the RT-1 pass in favour of the RT-1 pass.
A comparison of the treatments for 4 passes reveals
that there was a statistically significant difference
between the RT-4 passes and WT-4 passes, with less
compaction in the WT-4 passes only in one layer
(0.11–0.15 m). A statistically significant difference
between the RT-4 passes and WT-4 passes in favour
of the RT-4 passes existed only from 0.36 to 0.40 m
depth. This suggests that multiple passes made by the
two tractors cause very similar effects in the soil.
The values of dry bulk density between 0 and
0.20 m depth increased with the increase in the num-
ber of passes on the track, and all the differences
between the traffic treatments showed increases over
the control (Table 6). After 1 pass of the tractor, the
density increment ratio (Gn) over the control was the
same for wheeled and rubber-tracked tractors (4.8%),
while the highest values of density increment ratio was
found for rubber-tracked after 4 passes (17.7%) and
the difference between RT-4 and WT-4 was statisti-
cally significant in favour of WT treatment.
In spite of the fact that the rubber-tracked tractor
and wheeled tractor had a similar average ground
contact pressure, the greater penetration resistance
caused by the rubber-tracked tractor, especially in
the upper layers (Table 5) can be attributed both to
the lug shape and to the influence of the track forces on
the soil, the contact pressure distribution, the contact
pressure under the track supporting wheels, the track
roller reactions on links, and the track tension (Sofiyan
and Maximenko, 1965; Brusentsev, 1967; Rowland,
1972; Wong, 1993).
3.2. Soil shear strength
Soil shear strength results, measured at depths of
0–0.30 m in increments of 35 mm are shown in
Table 5
Mean values of soil layers of penetration resistance (MPa) as a result of 1 (RT-1; WT-1) and 4 passes (RT-4; WT-4)
Depth (m) Mean resistancea (MPa)
Control RT-1 RT-4 WT-1 WT-4
0–0.05 0.85 b 1.38 a, c 1.48 a, c 1.25 a, b 1.44 a, c
0.06–0.10 0.79 b 1.19 a 1.10 a, b 1.01 a, b 1.09 a, b
0.11–0.15 0.85 b 0.99 a 1.04 a 0.92 b 0.96 b
0.16–0.20 0.94 a 0.87 a 0.98 a, b 0.84 a 0.95 a, b
0.21–0.25 1.00 a 0.91 a 0.96 a 0.92 a 0.97 a
0.26–0.30 1.11 a 0.91 a 1.00 a, b 1.18 a, b 1.12 a
0.31–0.35 1.29 a 1.00 a 1.12 a, b 1.47 a, b 1.20 a, c
0.36–0.40 1.53 a 1.11 a 1.22 a 1.78 a, b 1.38 a, c
a Standard ANOVA test conducted, at the same depth of sample, between tractors for various number of passes and to the control plot and
between the two tractors for the same number of passes. Mean results are flanked on the same line by letters. Each two means which share a
letter do not differ significantly, level of significance �0.01 (Gomez and Gomez, 1976).
Table 6
Mean values of soil layers (0–0.20 m) of dry bulk density and its
increment ratio (Gn)
Treatments Dry bulk densitya (Mg m�3) Gn (%)
RT-1 1.3 a 4.8
RT-4 1.5 b 17.7
WT-1 1.3 a 4.8
WT-4 1.4 c 16.3
Control 1.2 d 0
a Standard ANOVA test conducted, at the same depth of
sample, between tractors for various number of passes and to the
control plot and between the two tractors for the same number of
passes. Mean results are flanked on the same line by letters. Each
two means which share a letter do not differ significantly, level of
significance �0.01 (Gomez and Gomez, 1976).
148 P. Servadio et al. / Soil & Tillage Research 61 (2001) 143–155
Fig. 1. In agreement with the results of penetrometer
and dry bulk density tests, the values of shear strength
increased with the increase in the number of passes on
the track, and for all treatments there were increases in
the upper soil layers (0–0.06 m).
A comparison of the mean shear strength for the two
tractors shows that in the upper layers (0–0.10 m), the
increases were higher for treatments WT both for 1
and 4 passes, in the layers (0.10–0.20 m), the increases
were particularly high for treatments RT-4 passes and
in the deeper layers (0.20–0.30), the increases were
particularly high for treatments WT-1 pass. This
proves that soil strength in these layers (from 0 to
0.30 depth in this case) for these types of tractors in the
same field conditions should be considered as being
significantly influenced.
A significant correlation ðp < 0:05Þ was found
between soil shear strength and dry bulk density for
single and multiple passes of tractors equipped with
both rubber tracks and with tires, both from 0 to
0.10 m and from 0.10 to 0.20 m depth (Figs. 2 and 3).
3.3. Macroporosity
Total macroporosity, expressed as a percentage of
area occupied by pores larger than 50 mm per thin
section, in the control and compacted areas is shown in
Fig. 4. In agreement with soil penetration resistance
results, the decrease of macroporosity in the surface
layer (0–0.10 m) was different after the passes of the
two tractors. The rubber-tracked tractor caused a
significant reduction of macroporosity after only 1
Fig. 1. Effects of soil compaction, caused by 1 (RT-1; WT-1) and 4 passes (RT-4; WT-4) of the two tractors (RT and WT), on shear strength in
the soil layer (0–0.30 m).
Fig. 2. Correlation between dry bulk density and shear strength in the soil surface layer (0–0.10 m).
P. Servadio et al. / Soil & Tillage Research 61 (2001) 143–155 149
pass, in comparison to the control area. After 4 passes,
the deleterious effect on macroporosity was more
evident. In fact, the total macroporosity was less than
10% and, according to the micromorphometric
method, such a soil is considered dense of compact
(Pagliai, 1988).
The wheeled tractor caused a significant reduction
of macroporosity only after 4 passes, and the porosity
was higher, even though not significantly, than that
measured in plots under 1 pass of rubber-tracked
tractor. The decrease of macroporosity after a single
pass of the wheeled tractor was not significant in
comparison to control areas.
The compacting effect of traffic by the two high-
power tractors seemed to be limited to the surface
layer: in fact, the macroporosity in the 0.10–0.20 m
layer did not show significant differences between
uncompacted areas and those compacted by 1 and 4
passes of the two tractors.
3.4. Pore shape and size distribution
Soil compaction following the passage of the two
tractors not only reduced total macroporosity but also
modified the soil pore system, i.e. modified the shape
and the size distribution of pores. Pore shape and size
Fig. 3. Correlation between dry bulk density and shear strength in the soil subsurface layer (0.10–0.20 m).
Fig. 4. Effects of soil compaction, caused by 1 (RT-1; WT-1) and 4 passes (RT-4; WT-4) of the two tractors (RT and WT), on soil
macroporosity expressed as a percentage of area occupied by pores larger than 50 mm per thin section. Average of six replicates. Each two
means which share a letter do not differ significantly ðp � 0:05Þ.
150 P. Servadio et al. / Soil & Tillage Research 61 (2001) 143–155
distribution in the 0–0.10 m layer of the areas com-
pacted by the passes of the two tractors showed large
differences compared with uncompacted areas (Fig. 5).
The reduction of porosity following the compaction by
1 and 4 passes of the tractors was due to the decrease in
the proportion of elongated pores. After 1 pass of the
wheeled tractor, the total elongated porosity value was
not significantly different in comparison to control
areas, but the size distribution was quite different. The
proportion of the elongated pores in the larger size
classes decreased and, in particular, pores of the 300–
500 mm size classes completely disappeared. The
elongated pores are the most important, because many
of these pores directly affect plant growth by easing
root penetration and storage and transmission of water
and gases. For example, according to Russell (1978)
and Tippkotter (1983), feeding roots need pores ran-
ging from 100 to 200 mm to grow into. According to
Greenland (1977), pores of equivalent pore diameter
ranging from 50 to 500 mm are the transmission pores
(elongated and continuous pores) which are important
both in soil–water–plant relationships and in main-
taining good soil structure conditions.
As was the case of total macroporosity, in the 0.10–
0.20 m layer, the pore shape and size distribution did
not show significant differences between the uncom-
pacted areas and those compacted by 1 or 4 passes of
the two tractors, thus confirming that the compacting
effect of machinery traffic was limited, in this soil, to
the surface layer.
3.5. Soil structure
Macroporosity, pore shape and size distribution
variations due to compaction by machinery traffic
were reflected in the type of soil structure. Micro-
scopic examination of thin sections showed that in the
uncompacted areas, a subangular blocky structure was
homogeneously present within the entire 0–0.20 m
layer, while in the 0–0.10 m layer of the compacted
areas the structure was more dense.
In this soil, there was no evidence of platy structure
formation even in the areas compacted by 4 passes of
both tractors, as generally found in compacted soils
(Marsili et al., 1998). However, damage to soil struc-
ture can be recognized by decreases in the proportion
of transmission pores, i.e. elongated and continuous
pores with equivalent diameters ranging from 50 to
500 mm (Greenland, 1977; Pagliai et al., 1983). A
massive structure was evident for samples subjected
to 4 passes of RT tractor, characterized by few and thin
elongated pores. Furthermore, these pores were scar-
cely connected, so hindering water infiltration and
increasing the risks, already high for this soil, for
water stagnation or surface runoff. In the 0.10–0.20 m
layer, there was always a massive structure; micro-
scopic examination of this layer in comparison to the
surface layer of uncompacted areas showed that the
differences were mainly due to the reduction of elon-
gated pores.
3.6. Correlation between soil macroporosity and
saturated hydraulic conductivity
Saturated hydraulic conductivity of the 0–0.10 m
layer decreased following the traffic of the two tractors
(Table 7) and the lowest values were found after the
pass of the rubber-tracked tractor. In the 4 passes of
this tractor (RT-4), the hydraulic conductivity was
drastically reduced in agreement with the low pre-
sence of elongated pores which were very thin and not
continuous in a vertical direction.
Fig. 6 shows a highly significant correlation
ðp < 0:01Þ between hydraulic conductivity and elon-
gated pores and a significant correlation with total
macroporosity. Since the elongated pores represented
the highest proportion of total macroporosity in the
control soils and the variation after compaction mainly
Table 7
Effect of soil compaction, caused by 1 (RT-1; WT-1) and 4 passes
(RT-4; WT-4) of the two tractors, on saturated hydraulic
conductivity in the surface soil layer (0–0.10 m)
Treatments Saturated hydraulic
conductivitya (mm h�1)
RT-1 3.3 a
RT-4 1.1 b
WT-1 11.2 c
WT-4 7.5 d
Control 18.5 e
a Standard ANOVA test conducted, at the same depth of
sample, between tractors for various number of passes and to the
control plot and between the two tractors for the same number of
passes. Mean results are flanked on the same line by letters. Each
two means which share a letter do not differ significantly, level of
significance �0.01 (Gomez and Gomez, 1976).
P. Servadio et al. / Soil & Tillage Research 61 (2001) 143–155 151
Fig. 5. Macropore size distribution, according to the equivalent pore diameter for regular and irregular pores, or the width for elongated pores,
in the surface soil layer (0–0.10 m).
caused a reduction of such pores, this result confirmed
that hydraulic conductivity is directly correlated with
elongated continuous pores. These results stressed that
the compaction is one of the most important aspects,
not only of soil degradation but also of environmental
degradation, since the strong reduction of water infil-
tration may increase the risks of soil erosion.
3.7. Relation between total macroporosity and soil
penetration resistance
Previous studies (Pagliai et al., 1992; Marsili et al.,
1998) on the effects of compaction caused by different
types of mobility system on total macroporosity and
soil structure would appear to have demonstrated a
good correlation in the compacted surface layer (0–
0.10 m) between macroporosity and soil penetration
resistance. Fig. 7 shows the relations ðp < 0:05Þ
between penetration resistance and total macroporos-
ity at 0–0.10 m depth for single and multiple passes of
tractors equipped with rubber tracks (RT-1 pass and
RT-4 passes) and with tires (WT-1 pass and WT-4
passes). The values can be represented by a linear type
regression, namely
y ¼ ax þ c (2)
where y is the penetration resistance in MPa, x the total
macroporosity expressed in %, a a coefficient, and c a
constant which, for single and multiple passes with the
rubber-tracked tractor, amount to a ¼ �0:0314 and
c ¼ þ1:6195, and for single and multiple passes with
the wheeled tractor amount to a1 ¼ �0:0487 and
c1 ¼ þ2:0887.
For the 0.10–0.20 m depth, the differences in por-
osity are not significant enough to find any relation-
ship with soil penetration resistance.
Fig. 6. Correlations between hydraulic conductivity and elongated pores and total porosity in the surface layer (0–0.10 m).
Fig. 7. Correlations between soil penetration resistance and macroporosity after single and multiple passes of tractors equipped with rubber
tracks and with tires in the soil layer (0–0.10 m depth).
P. Servadio et al. / Soil & Tillage Research 61 (2001) 143–155 153
These results indicate that in these test conditions,
the wheeled tractor caused less soil compaction and
resulted in a higher degree of macroporosity in the
surface layer than the rubber-tracked tractor.
4. Conclusions
Tests conducted on two high-powered tractors with
two different types of running gear allowed the eva-
luation of the degree of soil compaction by analysing
variation in some physical properties. After single and
multiple passes of the two tractors, statistically sig-
nificant differences in soil penetration resistance in
favour of the wheeled tractor were recorded only in the
surface layers, while a statistically significant differ-
ence in favour of the tracked tractor was found in the
deeper layers. The decrease in macroporosity, in
particular of elongated pores in the soil surface layer,
was greater in treatments involving the rubber-tracked
tractor than for the wheeled tractor. Hydraulic con-
ductivity of the surface layer was relatively low at the
test site as the soil is only slightly permeable, and was
inversely proportional to macroporosity and to elon-
gated pores. However, with respect to the higher
degree of macroporosity, treatments involving the
wheeled tractor showed better soil structure quality.
Tractors equipped with low aspect ratio tires give
rise to less soil damage than that following the passage
of rubber-tracked tractors, particularly on the upper
layers. A tractor equipped with rubber tracks of some-
what greater mass and power than the wheeled tractor
caused effects on the soil substantially equivalent to
those of the wheeled tractor, but with moderate
damage in the upper soil layers (0–0.20 m). This
can be attributed both to the stress action of the lugs
on the rubber track and to the compression caused by
the three track supporting wheels. Within the deeper
layers (from 0.20 to 0.40 m), an improvement of the
soil measured parameters in favour of the rubber-
tracked tractor was observed.
Acknowledgements
This work was carried out under the auspices of a
Concerted Action on subsoil compaction of the Com-
mission of the European Communities, Agriculture and
Fisheries (FAIR) specific RTD programme, FAIR5-
CT97-3589 ‘‘Experiences with the impact of subsoil
compaction on soil, crop growth and environment
and ways to prevent subsoil compaction’’. The authors
wish to thanks Dr. Olga Grasselli forherhelp inplanning
and collecting soil samples for porosity and hydraulic
conductivity measurements and Mr. Andrea Rocchini
for technical assistance in laboratory analysis.
References
Ahuja, L.R., Naney, J.W., Green, R.E., Nielson, D.R., 1984.
Macroporosity to characterise spatial variability hydraulic
conductivity and effects of land management. Soil Sci. Soc.
Am. J. 48, 699–702.
Arvidsson, J., Hakansson, I., 1996. Do effects of soil compaction
persist after ploughing? Results from 21 long-term field
experiments in Sweden. Soil Till. Res. 39, 175–197.
Bekker, M.G., 1969. Introduction to Terrain–Vehicle Systems.
University of Michigan Press, Ann Arbor, MI.
Bouma, J., Jongerius, A., Boersma, O.H., Jager, A., Schoonder-
beek, D., 1977. The function of different types of macropores
during saturated flow through four swelling soil horizons. Soil
Sci. Soc. Am. J. 41, 945–950.
Brown, H.J., Cruse, R.M., Erbach, D.C., Melvin, S.W., 1992.
Tractive device effects on soil physical properties. Soil Till.
Res. 22, 41–53.
Brusentsev, A.I., 1967. The tractive performance of tractors with
bulldozers. Terramechanics 4, 9–16.
Burt, E.C., Reaves, C.A., Bailey, A.C., Pickering, W.D., 1980. A
machine for testing tractor tires in soil bins. Trans. ASAE 23
(3), 546–552.
Cestelli Guidi, C., 1987. Geotecnica e Tecnica delle Fondazioni
(Geotechnique and Technique of the Foundation). Ulrico
Hoepli, Milano, pp. 98–113.
Dawidowski, J.B., Lerink, P., 1990. Laboratory simulation of the
effects of traffic during seedbed preparation on soil physical
properties using a quick uni-axial compression test. Soil Till.
Res. 17, 31–45.
Esch, J.H., Bashford, L.L., Von Bargen, K., Ekstrom, R.E., 1990.
Tractive performance comparisons between rubber belt track
and four-wheel-drive tractor. Trans. ASAE 33, 1109–1115.
FAO, 1988. FAO/UNESCO Soil Map of the World, Revised
Legend. World Resources Report 60. Food and Agriculture
Organization, Rome, 138 pp.
Fujii, H., 1992. Problems between soil and construction machinery
with special reference to field compaction. Terramechanics 29,
35–55.
Gomez, K.A., Gomez, A.A., 1976. Statistical Procedures for
Agricultural Research. The International Rice Research
Institute, Los Banos, Philippines, pp. 97–119.
Greenland, D.J., 1977. Soil damage by intensive arable cultiva-
tions: temporary or permanent? Phil. Trans. R. Soc. London
281, 193–208.
154 P. Servadio et al. / Soil & Tillage Research 61 (2001) 143–155
Klute, A., Dirksen, C., 1985. Hydraulic conductivity and
diffusivity: laboratory methods. In: Klute, A. (Ed.), Methods
of Soil Analysis, Part 1, 2nd Edition. American Society of
Agronomy Publication, Madison, WI, pp. 687–734.
Koolen, A.J., 1974. A method for soil compactibility determina-
tion. J. Agric. Eng. Res. 19, 271–278.
Koolen, A.J., 1987. Deformation and compaction of elemental soil
volumes and effects on mechanical properties. Soil Till. Res.
10, 5–19.
Koolen, A.J., Vaandrager, P., 1984. Relationships between soil
mechanical properties. J. Agric. Eng. Res. 29, 313–319.
Lowery, B., Schuler, R.T., 1994. Duration and effects of
compaction on soil and plant growth in Wisconsin. Soil Till.
Res. 29, 205–210.
Marsili, A., Servadio, P., 1992. Prove sul compattamento del
terreno agrario con due diversi tipi di pneumatici a confronto
(tests on agricultural soil compaction with two different
types of tyres in comparison). Rivista di Ingegneria Agraria
4, 193–199.
Marsili, A., Servadio, P., 1996. Compaction effects of rubber or
metal-tracked tractor passes on agricultural soils. Soil Till. Res.
37, 37–45.
Marsili, A., Servadio, P., Pagliai, M., Vignozzi, N., 1998. Changes
of some physical properties of a clay soil following passage of
rubber- and metal-tracked tractors. Soil Till. Res. 49, 185–199.
Murphy, C.P., 1986. Thin Section Preparation of Soils and
Sediments, 1st Edition. AB Academic Publishers, Herts, UK.
Ohu, J.O., Raghavan, G.S.V., McKyes, E., Mehuys, G., 1986. Shear
strength prediction of compacted soil with varying added
organic matter contents. Trans. ASAE 29, 351–355.
O’Sullivan, M.F., 1992. Uniaxial compaction effects on soil
physical properties in relation to soil type and cultivation. Soil
Till. Res. 24, 257–269.
Pagliai, M., 1988. Soil porosity aspects. Int. Agrophys. 4, 215–232.
Pagliai, M., La Marca, M., Lucamante, G., 1983. Micromorpho-
metric and micromorphological investigations of a clay loam
soil in viticulture under zero and conventional tillage. Soil Sci.
34, 391–403.
Pagliai, M., La Marca, M., Lucamante, G., Genovese, L., 1984.
Effects of zero and conventional tillage on the length and
irregularity of elongated pores in a clay loam soil under
viticulture. Soil Till. Res. 4, 433–444.
Pagliai, M., Febo, P., La Marca, M., Lucamante, G., 1992. Effetti
del compattamento provocato da differenti tipi di pneumatici su
porosita e struttura del terreno (Compaction effects caused from
different types of tyres on macroporosity and soil structure).
Rivista di Ingegneria Agraria 3, 168–176.
Raghavan, G.S.V., McKyes, E., Beaulieu, B., 1978. Clay soil
compaction due to wheel slip. Trans. ASAE 21, 646–653.
Rowland, D., 1972. Tracked vehicle ground pressure and its effect
on soft ground performance. In: Proceedings of the Fourth
International Conference on Terrain–Vehicle Systems, Stock-
holm, Sweden, pp. 353–384.
Russell, E.W., 1978. Arable agriculture and soil deterioration. In:
Transactions of the 11th International Congress of Soil
Science, Vol. 3, June 19–27, 1978, University of Alberta,
Edmonton. Canadian Society of Soil Science, Alberta,
pp. 216–227.
Schafer, R.L., Johnson, C.E., 1990. Soil dynamics and cropping
systems. Soil Till. Res. 16, 143–152.
Soane, B.D., Van Ouwerkerk, C. (Eds.), 1994a. Soil Compaction in
Crop Production: Developments in Agricultural Engineering,
Vol. 11. Elsevier, Amsterdam, 662 pp.
Soane, B.D., Van Ouwerkerk, C. (Eds.), 1994b. Soil compaction
problems in world agriculture. Soil Compaction in Crop
Production: Developments in Agricultural Engineering, Vol.
11. Elsevier, Amsterdam, pp. 1–26.
Soane, B.D., Van Ouwerkerk, C., 1995. Implications of soil
compaction in crop production for quality of the environment.
Soil Till. Res. 35, 5–22.
Sofiyan, A.P., Maximenko, Ye.I., 1965. The distribution of pressure
under a tracklaying vehicle. Terramechanics 2, 11–16.
Terzaghi, K., Peck, R.B., 1979. Geotecnica (Geotechnique).
Unione tipografico-Editrice Torinese, Torino.
Tippkotter, R., 1983. Morphology, spatial arrangement and origin
of macropores in some Hapludalfs, West Germany. Geoderma
29, 355–371.
Verma, B.P., Bailey, A.C., Schafer, R.L., Futral, J.G., 1976. A
pressure transducer in soil compaction study. Trans. ASAE 19,
442–447.
Walkley, A., Black, I.A., 1934. An examination of Degijareff
method for determining soil organic matter and proposed
modification of the chromic acid titration method. Soil Sci. 63,
251–264.
Way, T.R., Bailey, A.C., Raper, R.L., Burt, E.C., 1995. Tire lug
height effect on soil stresses and bulk density. Trans. ASAE 38,
669–674.
Wiermann, C., Way, T.R., Horn, R., Bailey, A.C., Burt, E.C., 1999.
Effects of various dynamic load on stress and strain behavior of
a Norfolk sandy loam. Soil Till. Res. 50, 127–135.
Willatt, S.T., 1987. Influence of aggregate size and water content
on compactability of soil using short-time static load. J. Agric.
Eng. Res. 37, 107–115.
Wong, J.Y., 1993. Theory of Ground Vehicles. Wiley, New York.
P. Servadio et al. / Soil & Tillage Research 61 (2001) 143–155 155