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Int. J. Pure Appl. Sci. 1:9-15 (2015)
Research/Araştırma
9
Hydraulic Properties Estimation of an Experimental Urban Soil Column
Constructed with Waste Brick and Compost
Deniz Yilmaz1*
, Murat Dal2
1
LUNAM Université, IFSTTAR, GER, Bouguenais, F-44341, France
2
Tunceli University, Engineering Faculty, Civil Engineering Department, Tunceli, Turkey
*Corresponding author: E-mail: dyilmaz@tunceli.edu.tr
Abstract
For sustainable development, cities have to revalorize waste material produced
by human activities. Urban soils could be constructed from waste material such as
bricks or concrete waste and mixed with compost material for greening application in
urban environment. This study proposes to study from hydraulically point of view an
experimental urban soil constructed with waste brick and compost using an adapted
evaporation laboratory method. The hydraulic properties are estimated using Hydrus 1D
code inverse procedure and are compared with classical soils such as sand, loam and
silt. Conclusions are promising but more investigation should be done to confirm the
possibility of using this material as urban soil for greening application in cities.
Key words: Evaporation Experiment, Hydrus 1D, Hydraulic Properties, Urban Soil
Atık Tuğla ve Kompost ile İnşa Edilen Deneysel Bir Zeminin Hidrolik
Karakteristiklerinin Buharlaşma Metodu ile Tespiti
Özet
Kentlerin sürdürülebilirliği için, kendi atıklarını yeniden değerlendirmesi ile
mümkündür. Özellikle kentsel dönüşüm projelerinde inşaat atıklarının değerlendirmesi
önem arz etmektedir. Kentsel zeminler atık tuğla, atık beton gibi malzemeler ile inşa
edilebilir. Bunlara yeşillendirme fonksiyonu verilebilmesi içinde atık malzemelere
kompost eklenebilinir. Bu çalışmada laboratuarda buharlaşma metodu yöntemini
kullanarak atık tuğla ve kompost ile inşa edilmiş, deneysel bir zeminin hidrolik açıdan
incelenmesi ve karakteristiklerinin tespiti amaçlanmıştır. Hidrolik özellikler; Hydrus 1D
kodunun inverse prosedürü kullanılarak tespit edilmiştir. Kum, kil ve silt gibi klasik
zeminlerin karakteristikleri ile karşılaştırılmıştır. Bu zeminler hem mekanik, hem
hidrolik ve hem de biyolojik açıdan ele alınarak, şehir zeminlerinde uygulanması söz
konusudur.
Anahtar kelimeler: Buharlaşma metodu, Hydrus 1D, Hidrolik özellikler, Şehir zemini
INTRODUCTION
Cities are renewing continuously
by demolition of old construction. This
process is producing wastes of
demolition such as bricks, concrete,
ballast of railway track, excavated soils.
These wastes are consistently exported
out of the city and are land filled or
parts of them are recycled (Marshall and
Farahbakhsh, 2013). For example, the
amount of waste material stemming
from civil engineering activities in
France is 253 million tons for 2009
(ADEME, 2012). For Turkey, there is
no net data regarding the amount of
demolition waste (Esin and Cosgun,
Int. J. Pure Appl. Sci. 1:9-15 (2015)
Research/Araştırma
10
2007). After the earthquake of 1999 in
Marmara region 13 million of waste
material occurred (Esin and Cosgun,
2007). The construction and demolition
waste are estimated of 200 kg per
person per year in Turkey (Arslan et al.,
2012). Since one year, a big project of
demolition of old construction in
Turkey is planned for sustainable city
retrofitting named as ‘kentsel Dönüşüm’
in Turkish. Thus the amount of
demolition waste creates will increase
in Turkey and will be a huge issue of
waste management. In other part, cities
are also producing compost material
and green wastes from maintenance of
gardens and parks which can provide
nutriments for vegetation in an urban
soil matrix. City practitioners are
usually building urban soils from
agricultural soil stripping and
aggregates coming from quarries. One
alternative idea is to reuse the waste
material produced by the city as urban
soils for parks, gardens and tree lines.
SITERRE project was launched and
funded by the French environmental
agency (ADEME) to develop the
knowledge on urban soils built with
waste material. A part of the project is
focusing on the feasibility to reuse
waste brick mixed with organic matter
(compost and green waste) for plant
growth and trees in urban environment.
These urban soils have to display
adequate properties with respect to their
bearing capacity in an urban
environment, their agronomic properties
for plant growth, their drainage capacity
and the environmental restrictions
enforced by the French regulation in
order to prevent pollutant release in the
underlying aquifer.
The knowledge of hydraulic
properties of urban soils is very
important to understand hydraulic
functioning of urban areas. These are
necessary for modeling hydrologic
processes at the city scale for rainwater
management purposes (Mitchell et al.,
2001; Dussaillant et al., 2004;
Lassabatere et al., 2010), for modeling
the evapotranspiration of trees to assess
their impact on urban climate (House-
Peters and Chang, 2011) and its effect
on the urban heat island phenomenon,
and also for modeling the pollutant
transfer where it is known that water
flow is the main vector of transportation
for pollutants (Lassabatere et al., 2007;
Lamy et al., 2009, Yilmaz et al., 2010).
These properties are also important to
understand if the materials have ability
for agronomic purposes. Hydrodynamic
properties of urban soils built with
waste material are rarely studied and not
very well known. Only a few studies
tried to focus on hydraulic properties
(Sere et al., 2012; Ojeda et al., 2011) of
urban soils built from waste material.
As means of hydraulic
characterization at the laboratory scale,
the evaporation method through
analysis of experimental pressure heads
at different heights in a vertical column
has become widespread in obtaining
hydraulic properties for soils (Wind,
1968; Tamari et al., 1993; Simunek et
al., 1998; Yilmaz et al., 2010).
The aim of this work is the
characterization of hydraulic parameters
of urban soil built from brick waste and
compost using an adapted wind
laboratory method.
MATERIAL AND METHODS
Studied Materials
The studied material noted Br-
Co (Br: Brick waste and Co: compost)
was built from a mixture of 60 wt.% of
brick (Br) fabrication waste and 40
wt.% of compost (Co) coming from
waste management facilities and waste
composting. Its specific density was
Int. J. Pure Appl. Sci. 1:9-15 (2015)
Research/Araştırma
11
estimated in laboratory using
picnometer method to 2.18 g.cm-3
.
The Adapted Evaporation Method
The column configuration for
the evaporation experiment used in this
study is different than the conventional
method known as Wind method (Wind,
1968). For this reason, the method used
in this study is mentioned as adapted
evaporation method. In laboratory, the
studied material was packed into 40 cm
high and 7 cm radius column, placed on
a monitored balance (Figure 1). Three
tensiometers (T5, Ums Gmbh, Münich,
Germany), with cups of 7 cm long and
0.5 cm in diameter were horizontally
inserted into drill holes in the material
core at 8.5 cm, 10 and 11.5 cm from
the sample surface.
Figure 1. Adapted evaporation column
experiment.
The system was saturated with water
during a sufficient time to reach
hydraulic equilibrium. The
measurement of the mass was
performed by weighing with mass
balance every hour and the
measurements of pressure heads each
five minutes. The potential evaporation
rate was measured every hour using a
square tank filled with water, this
system was placed on monitored
balance and the weighting
measurements were done every hour.
Both balance system were connected to
a computer for data collection.
Tensiometers were connected to a data
logger CR10X from Campbell scientific
for data collection. Initial pressure head
of -10 cm for the tensiometer at 8.5 cm
was measured. The experiment was
performed till the water pressure heads
reach the pressure head of -800 cm. The
experiment lasted 5 months. At the end,
the material was extracted from the
columns and dried to determinate the
water content profile with 5 points.
Modeling was performed using
HYDRUS 1D code (Simunek and al.,
2008) that resolves the Richards’
equation. The unsaturated soil hydraulic
properties are described by the Van
Genuchten (equation 1 and 3) model in
junction with Mualem capillary model
(equation 2).
The evaporation experiment
setup was simulated through a 40 cm
length mesh with 0.1 cm length
elements. Observation points were
introduced at the tensiometer depths.
The initial condition corresponded to
pressure equilibrium with 0 cm at the
surface and 40 cm water pressure head
at the bottom. The boundary conditions
correspond to no flux at the bottom and
daily measured potential evaporation
rate. The hydraulic parameters were
estimated through the HYDRUS 1D
inverse procedure (Marquardt, 1963).
The data to be fitted correspond to the
evolution of the pressure heads at the
observation points and the total water
loss at the end of the experiment.
Int. J. Pure Appl. Sci. 1:9-15 (2015)
Research/Araştırma
12
Hydraulic parameters
Van Genuchten-Mualem
(Mualem, 1976; Van Genuchten, 1980)
models are used to describe the
hydrodynamic functions h(θ) and K(θ)
in Hydrus.
mn
grs
r
h
h




















1


[1]
1
1m
n
  [2]
2
1/
( ) 1 1
ml m
r r
s
s r s r
K K
   

   
                     
[3]
where n, m are the hydraulic shape
parameters, s and r are the saturated
and residual water contents
respectively, hg the scale parameter for
water pressure head, and Ks the
saturated hydraulic conductivity. The
parameter l is the pore connectivity
parameter and it’s usually set to the
value of 0.5 [-].
The saturated water content is
supposed equal to the porosity and is
estimated from both the dry bulk ( d )
and specific ( s ) densities through the
following equation:
s
d
s


 1 [6]
RESULTS AND DISCUSSIONS
Particle Size Distribution
The particle size distribution
(PSD) analysis, involving manual
sieving and complemented by a grain
size analyzer, is illustrated in figure 2.
The percentages according the U.S.D.A
(U.S Department of Agriculture) above
2 mm fractions (gravel), between 0.05
and 2 mm (sand), between 0.05 and
0.002 mm (silt), and less than 0.05 mm
(clay) are 58.3%, 31.3%, 10.2% and
0.2%. Br-Co material is composed with
large pieces of bricks and this explains
the high value of the percentage of
gravel.
Figure 2. Particle size distribution of
studied material.
Adapted Evaporation Column
Experiment and Inversion Results
The experiment started the 25th
November 2013 and was stopped the 11
April 2014 after the upper tensiometer
has reached the value of -800 cm in
pressure head. The figure 3 is showing
the time evolution of pressure head at -
8.5, 10.0 and 11.5 cm level for the
surface of the evaporation column and
the corresponding model estimation
from Hydrus 1D software. For the
inverse procedure, the saturated water
content θs (cm3
.cm-3
) was fixed and
calculated to 0.631 through equation
n°6. At the end of the evaporation
experiment, the material was dried and
the dry bulk density was estimated to
0.80 g.cm-3
. The residual water content
was fixed to 0.1 cm3
.cm-3
. The initial
water content was supposed equal to the
saturated water content. The inversion
results are shown in table 1.
Int. J. Pure Appl. Sci. 1:9-15 (2015)
Research/Araştırma
13
Table 1. Br-Co material hydraulics parameters estimated from inversion of data
collected from the adapted evaporation experiment
Hydraulics parameters
θr
(cm3
.cm-3
)
θs
(cm3
.cm-3
)
|hg|
(cm)
n
(-)
Ks
(cm.h-1
)
Br-Co studied material 0.1 0.631 12.8 1.43 29.0
The model gives similar values
of pressure head for the three heads up
to pressure head of -300 cm. After that,
the differences between the three heads
are more distinct. The fit of the model
on experimental data are reproducing
the experimental tendency.
Figure 3. Evaporation experiment
results of pressure head monitoring at
level -8.5 cm. 10.0 cm and 11.5 cm
from the top of the column and models
corresponding to the inverse procedure.
Discussions
For purpose of discussion,
hydrodynamic curves h(θ) and K(θ) of
the studied Br-Co material are displayed
respectively in figure 4 and 5. In order
to compare this material with classical
soils such as a sandy, loam and silt,
their hydrodynamics curves are also
reproduced. For that, we used the
hydraulic parameters proposed in
HYDRUS database for sand, loam and
silt.
Figure 4. Water retention curves,
Volumetric water content [cm3
.cm-3
] on
horizontal axe and absolute pressure
head [cm] for vertical axe displayed in
logarithm scale.
The studied material Br-Co has his
saturated volumetric water content θs
higher than classical natural soil or
cultivated soil. This could be explained
by the high content of organic matter in
the material. Organic matter is well
known for its important total porosity
ranging from 0.7 cm3
.cm-3
for composts
material to 0.9 cm3
.cm-3
for peat
material (Cannavo and Michel, 2013).
Br-Co material absolute pressure head
for volumetric water content in very dry
condition (<0.15 cm3
.cm-3
) is lower
than those of classical soil. For
volumetric water content upper than
0.15 cm3
.cm-3
, absolute pressure head of
Br-Co material are contained between
thus of silt soil and loam soil.
For hydraulic conductivity
curves, the same tendency of retention
curves is observed. For dry condition,
the hydraulic conductivity of the studied
material is lower than thus of classic
-890
-790
-690
-590
-490
-390
-290
-190
-90
10
0 20 40 60 80 100 120 140 160
T_8.5
Model_8.5
T_10.0
Model_10.0
T_11.5
Model_11.5
Time (d)
Succion (cm)
Int. J. Pure Appl. Sci. 1:9-15 (2015)
Research/Araştırma
14
soils. For volumetric water content
upper than 0.2 cm3
.cm-3
hydraulic
conductivity K is contained between the
K of a silt and loam soil.
Figure 5. Hydraulic conductivity
curves, Volumetric water content [-] on
horizontal axe and water conductivity
[cm.h-1
] for vertical axe in logarithm
scale.
From hydraulic point of view,
this material is functioning between a
silt soil and loam soil. It could be used
as an urban soil for greening purposes
(for instance, for tree or grass growth)
but this has to be studied by
experimental application of greening.
CONCLUSION
The studied material Br-Co was
constructed with a mixture of waste
fabrication bricks and compost to be
used as an urban soil for greening
purpose such as grass or tree. The
hydraulic properties of this material
were obtained through an adapted
evaporation experiment and
experimental collected data were
inversed using Hydrus 1D code. The
estimated hydraulics properties permit
to classify the studied material from
hydraulics point of view between a
loam and a silty soil. This experimental
urban soil material have high porosity
and high hydraulic conductivity value
of Ks and it can achieve the role of
urban soil for greening purpose like
gardens, parks and trees lines, but more
additional study has to be done like
greening experimental plot in situ to
verify the feasibility. Also, an
environmental impact study has to been
done before using this material as urban
soil. For Turkey, demolition waste
could be also valorized as urban soil.
Further research on hydraulics
properties of urban soil constructed with
waste demolition material coming from
Turkish market has to be done and
feasibility of the reuse as urban soil as
to be checked. Finally, the proposed
hydraulics properties of this study can
be used for the settings of urban soil
hydraulic parameters in multiple
applications as water modelling,
evapotranspiration modelling or
pollutant transfer study at the city scale.
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(Edition 2012).
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Dussaillant, A.R., Wu, C.H., Potter, K.W.,
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House-Peters, L.A., Chang, H., 2011.
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Marquardt, D.W., 1963. An algorithm for
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Marshall, R.E., Farahbakhsh., K., 2013.
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technosol.Vadose Zone Journal..
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Van Genuchten, M.T., 1980. A closed form
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Hydraulic properties estimation of an experimental urban soil column constructed with waste brick and compost Doç.Dr.Murat DAL

  • 1. Int. J. Pure Appl. Sci. 1:9-15 (2015) Research/Araştırma 9 Hydraulic Properties Estimation of an Experimental Urban Soil Column Constructed with Waste Brick and Compost Deniz Yilmaz1* , Murat Dal2 1 LUNAM Université, IFSTTAR, GER, Bouguenais, F-44341, France 2 Tunceli University, Engineering Faculty, Civil Engineering Department, Tunceli, Turkey *Corresponding author: E-mail: dyilmaz@tunceli.edu.tr Abstract For sustainable development, cities have to revalorize waste material produced by human activities. Urban soils could be constructed from waste material such as bricks or concrete waste and mixed with compost material for greening application in urban environment. This study proposes to study from hydraulically point of view an experimental urban soil constructed with waste brick and compost using an adapted evaporation laboratory method. The hydraulic properties are estimated using Hydrus 1D code inverse procedure and are compared with classical soils such as sand, loam and silt. Conclusions are promising but more investigation should be done to confirm the possibility of using this material as urban soil for greening application in cities. Key words: Evaporation Experiment, Hydrus 1D, Hydraulic Properties, Urban Soil Atık Tuğla ve Kompost ile İnşa Edilen Deneysel Bir Zeminin Hidrolik Karakteristiklerinin Buharlaşma Metodu ile Tespiti Özet Kentlerin sürdürülebilirliği için, kendi atıklarını yeniden değerlendirmesi ile mümkündür. Özellikle kentsel dönüşüm projelerinde inşaat atıklarının değerlendirmesi önem arz etmektedir. Kentsel zeminler atık tuğla, atık beton gibi malzemeler ile inşa edilebilir. Bunlara yeşillendirme fonksiyonu verilebilmesi içinde atık malzemelere kompost eklenebilinir. Bu çalışmada laboratuarda buharlaşma metodu yöntemini kullanarak atık tuğla ve kompost ile inşa edilmiş, deneysel bir zeminin hidrolik açıdan incelenmesi ve karakteristiklerinin tespiti amaçlanmıştır. Hidrolik özellikler; Hydrus 1D kodunun inverse prosedürü kullanılarak tespit edilmiştir. Kum, kil ve silt gibi klasik zeminlerin karakteristikleri ile karşılaştırılmıştır. Bu zeminler hem mekanik, hem hidrolik ve hem de biyolojik açıdan ele alınarak, şehir zeminlerinde uygulanması söz konusudur. Anahtar kelimeler: Buharlaşma metodu, Hydrus 1D, Hidrolik özellikler, Şehir zemini INTRODUCTION Cities are renewing continuously by demolition of old construction. This process is producing wastes of demolition such as bricks, concrete, ballast of railway track, excavated soils. These wastes are consistently exported out of the city and are land filled or parts of them are recycled (Marshall and Farahbakhsh, 2013). For example, the amount of waste material stemming from civil engineering activities in France is 253 million tons for 2009 (ADEME, 2012). For Turkey, there is no net data regarding the amount of demolition waste (Esin and Cosgun,
  • 2. Int. J. Pure Appl. Sci. 1:9-15 (2015) Research/Araştırma 10 2007). After the earthquake of 1999 in Marmara region 13 million of waste material occurred (Esin and Cosgun, 2007). The construction and demolition waste are estimated of 200 kg per person per year in Turkey (Arslan et al., 2012). Since one year, a big project of demolition of old construction in Turkey is planned for sustainable city retrofitting named as ‘kentsel Dönüşüm’ in Turkish. Thus the amount of demolition waste creates will increase in Turkey and will be a huge issue of waste management. In other part, cities are also producing compost material and green wastes from maintenance of gardens and parks which can provide nutriments for vegetation in an urban soil matrix. City practitioners are usually building urban soils from agricultural soil stripping and aggregates coming from quarries. One alternative idea is to reuse the waste material produced by the city as urban soils for parks, gardens and tree lines. SITERRE project was launched and funded by the French environmental agency (ADEME) to develop the knowledge on urban soils built with waste material. A part of the project is focusing on the feasibility to reuse waste brick mixed with organic matter (compost and green waste) for plant growth and trees in urban environment. These urban soils have to display adequate properties with respect to their bearing capacity in an urban environment, their agronomic properties for plant growth, their drainage capacity and the environmental restrictions enforced by the French regulation in order to prevent pollutant release in the underlying aquifer. The knowledge of hydraulic properties of urban soils is very important to understand hydraulic functioning of urban areas. These are necessary for modeling hydrologic processes at the city scale for rainwater management purposes (Mitchell et al., 2001; Dussaillant et al., 2004; Lassabatere et al., 2010), for modeling the evapotranspiration of trees to assess their impact on urban climate (House- Peters and Chang, 2011) and its effect on the urban heat island phenomenon, and also for modeling the pollutant transfer where it is known that water flow is the main vector of transportation for pollutants (Lassabatere et al., 2007; Lamy et al., 2009, Yilmaz et al., 2010). These properties are also important to understand if the materials have ability for agronomic purposes. Hydrodynamic properties of urban soils built with waste material are rarely studied and not very well known. Only a few studies tried to focus on hydraulic properties (Sere et al., 2012; Ojeda et al., 2011) of urban soils built from waste material. As means of hydraulic characterization at the laboratory scale, the evaporation method through analysis of experimental pressure heads at different heights in a vertical column has become widespread in obtaining hydraulic properties for soils (Wind, 1968; Tamari et al., 1993; Simunek et al., 1998; Yilmaz et al., 2010). The aim of this work is the characterization of hydraulic parameters of urban soil built from brick waste and compost using an adapted wind laboratory method. MATERIAL AND METHODS Studied Materials The studied material noted Br- Co (Br: Brick waste and Co: compost) was built from a mixture of 60 wt.% of brick (Br) fabrication waste and 40 wt.% of compost (Co) coming from waste management facilities and waste composting. Its specific density was
  • 3. Int. J. Pure Appl. Sci. 1:9-15 (2015) Research/Araştırma 11 estimated in laboratory using picnometer method to 2.18 g.cm-3 . The Adapted Evaporation Method The column configuration for the evaporation experiment used in this study is different than the conventional method known as Wind method (Wind, 1968). For this reason, the method used in this study is mentioned as adapted evaporation method. In laboratory, the studied material was packed into 40 cm high and 7 cm radius column, placed on a monitored balance (Figure 1). Three tensiometers (T5, Ums Gmbh, Münich, Germany), with cups of 7 cm long and 0.5 cm in diameter were horizontally inserted into drill holes in the material core at 8.5 cm, 10 and 11.5 cm from the sample surface. Figure 1. Adapted evaporation column experiment. The system was saturated with water during a sufficient time to reach hydraulic equilibrium. The measurement of the mass was performed by weighing with mass balance every hour and the measurements of pressure heads each five minutes. The potential evaporation rate was measured every hour using a square tank filled with water, this system was placed on monitored balance and the weighting measurements were done every hour. Both balance system were connected to a computer for data collection. Tensiometers were connected to a data logger CR10X from Campbell scientific for data collection. Initial pressure head of -10 cm for the tensiometer at 8.5 cm was measured. The experiment was performed till the water pressure heads reach the pressure head of -800 cm. The experiment lasted 5 months. At the end, the material was extracted from the columns and dried to determinate the water content profile with 5 points. Modeling was performed using HYDRUS 1D code (Simunek and al., 2008) that resolves the Richards’ equation. The unsaturated soil hydraulic properties are described by the Van Genuchten (equation 1 and 3) model in junction with Mualem capillary model (equation 2). The evaporation experiment setup was simulated through a 40 cm length mesh with 0.1 cm length elements. Observation points were introduced at the tensiometer depths. The initial condition corresponded to pressure equilibrium with 0 cm at the surface and 40 cm water pressure head at the bottom. The boundary conditions correspond to no flux at the bottom and daily measured potential evaporation rate. The hydraulic parameters were estimated through the HYDRUS 1D inverse procedure (Marquardt, 1963). The data to be fitted correspond to the evolution of the pressure heads at the observation points and the total water loss at the end of the experiment.
  • 4. Int. J. Pure Appl. Sci. 1:9-15 (2015) Research/Araştırma 12 Hydraulic parameters Van Genuchten-Mualem (Mualem, 1976; Van Genuchten, 1980) models are used to describe the hydrodynamic functions h(θ) and K(θ) in Hydrus. mn grs r h h                     1   [1] 1 1m n   [2] 2 1/ ( ) 1 1 ml m r r s s r s r K K                                [3] where n, m are the hydraulic shape parameters, s and r are the saturated and residual water contents respectively, hg the scale parameter for water pressure head, and Ks the saturated hydraulic conductivity. The parameter l is the pore connectivity parameter and it’s usually set to the value of 0.5 [-]. The saturated water content is supposed equal to the porosity and is estimated from both the dry bulk ( d ) and specific ( s ) densities through the following equation: s d s    1 [6] RESULTS AND DISCUSSIONS Particle Size Distribution The particle size distribution (PSD) analysis, involving manual sieving and complemented by a grain size analyzer, is illustrated in figure 2. The percentages according the U.S.D.A (U.S Department of Agriculture) above 2 mm fractions (gravel), between 0.05 and 2 mm (sand), between 0.05 and 0.002 mm (silt), and less than 0.05 mm (clay) are 58.3%, 31.3%, 10.2% and 0.2%. Br-Co material is composed with large pieces of bricks and this explains the high value of the percentage of gravel. Figure 2. Particle size distribution of studied material. Adapted Evaporation Column Experiment and Inversion Results The experiment started the 25th November 2013 and was stopped the 11 April 2014 after the upper tensiometer has reached the value of -800 cm in pressure head. The figure 3 is showing the time evolution of pressure head at - 8.5, 10.0 and 11.5 cm level for the surface of the evaporation column and the corresponding model estimation from Hydrus 1D software. For the inverse procedure, the saturated water content θs (cm3 .cm-3 ) was fixed and calculated to 0.631 through equation n°6. At the end of the evaporation experiment, the material was dried and the dry bulk density was estimated to 0.80 g.cm-3 . The residual water content was fixed to 0.1 cm3 .cm-3 . The initial water content was supposed equal to the saturated water content. The inversion results are shown in table 1.
  • 5. Int. J. Pure Appl. Sci. 1:9-15 (2015) Research/Araştırma 13 Table 1. Br-Co material hydraulics parameters estimated from inversion of data collected from the adapted evaporation experiment Hydraulics parameters θr (cm3 .cm-3 ) θs (cm3 .cm-3 ) |hg| (cm) n (-) Ks (cm.h-1 ) Br-Co studied material 0.1 0.631 12.8 1.43 29.0 The model gives similar values of pressure head for the three heads up to pressure head of -300 cm. After that, the differences between the three heads are more distinct. The fit of the model on experimental data are reproducing the experimental tendency. Figure 3. Evaporation experiment results of pressure head monitoring at level -8.5 cm. 10.0 cm and 11.5 cm from the top of the column and models corresponding to the inverse procedure. Discussions For purpose of discussion, hydrodynamic curves h(θ) and K(θ) of the studied Br-Co material are displayed respectively in figure 4 and 5. In order to compare this material with classical soils such as a sandy, loam and silt, their hydrodynamics curves are also reproduced. For that, we used the hydraulic parameters proposed in HYDRUS database for sand, loam and silt. Figure 4. Water retention curves, Volumetric water content [cm3 .cm-3 ] on horizontal axe and absolute pressure head [cm] for vertical axe displayed in logarithm scale. The studied material Br-Co has his saturated volumetric water content θs higher than classical natural soil or cultivated soil. This could be explained by the high content of organic matter in the material. Organic matter is well known for its important total porosity ranging from 0.7 cm3 .cm-3 for composts material to 0.9 cm3 .cm-3 for peat material (Cannavo and Michel, 2013). Br-Co material absolute pressure head for volumetric water content in very dry condition (<0.15 cm3 .cm-3 ) is lower than those of classical soil. For volumetric water content upper than 0.15 cm3 .cm-3 , absolute pressure head of Br-Co material are contained between thus of silt soil and loam soil. For hydraulic conductivity curves, the same tendency of retention curves is observed. For dry condition, the hydraulic conductivity of the studied material is lower than thus of classic -890 -790 -690 -590 -490 -390 -290 -190 -90 10 0 20 40 60 80 100 120 140 160 T_8.5 Model_8.5 T_10.0 Model_10.0 T_11.5 Model_11.5 Time (d) Succion (cm)
  • 6. Int. J. Pure Appl. Sci. 1:9-15 (2015) Research/Araştırma 14 soils. For volumetric water content upper than 0.2 cm3 .cm-3 hydraulic conductivity K is contained between the K of a silt and loam soil. Figure 5. Hydraulic conductivity curves, Volumetric water content [-] on horizontal axe and water conductivity [cm.h-1 ] for vertical axe in logarithm scale. From hydraulic point of view, this material is functioning between a silt soil and loam soil. It could be used as an urban soil for greening purposes (for instance, for tree or grass growth) but this has to be studied by experimental application of greening. CONCLUSION The studied material Br-Co was constructed with a mixture of waste fabrication bricks and compost to be used as an urban soil for greening purpose such as grass or tree. The hydraulic properties of this material were obtained through an adapted evaporation experiment and experimental collected data were inversed using Hydrus 1D code. The estimated hydraulics properties permit to classify the studied material from hydraulics point of view between a loam and a silty soil. This experimental urban soil material have high porosity and high hydraulic conductivity value of Ks and it can achieve the role of urban soil for greening purpose like gardens, parks and trees lines, but more additional study has to be done like greening experimental plot in situ to verify the feasibility. Also, an environmental impact study has to been done before using this material as urban soil. For Turkey, demolition waste could be also valorized as urban soil. Further research on hydraulics properties of urban soil constructed with waste demolition material coming from Turkish market has to be done and feasibility of the reuse as urban soil as to be checked. Finally, the proposed hydraulics properties of this study can be used for the settings of urban soil hydraulic parameters in multiple applications as water modelling, evapotranspiration modelling or pollutant transfer study at the city scale. REFERENCES Ademe. 2012. Les déchets- Chiffres Clés (Edition 2012). Arslan, H., Salgın, B., Coşgun, N., 2012. Construction and demolition waste management in Turkey. INTECH Open Access Publisher. Cannavo, P., Michel. J.C., 2013. Peat particle size effects on spatial root distribution and changes on hydraulic and aeration properties. Scientia Horticulturae, 151:11-21 Dussaillant, A.R., Wu, C.H., Potter, K.W., 2004. Richards equation model of a rain garden. Journal of Hydrologic Engineering, 9(3): 219-225. Esin, T., Cosgun, N., 2007. A study conducted to reduce construction waste generation in Turkey. Building and Environment, 42(4), 1667-1674. House-Peters, L.A., Chang, H., 2011. Modeling the impact of land use and climate change on neighborhood-scale evaporation and nighttime cooling: A surface energy balance approach. Landscape and Urban Planning, 103(2):139-155. Lamy, E., Lassabatere, L., Bechet, B., Andrieu, H., 2009. Modeling the influence of an artificial macropore in
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