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International Journal of Civil Engineering and Technology (IJCIET)
Volume 7, Issue 1, Jan-Feb 2016, pp. 304-314, Article ID: IJCIET_07_01_025
Available online at
http://www.iaeme.com/IJCIET/issues.asp?JType=IJCIET&VType=7&IType=1
Journal Impact Factor (2016): 9.7820 (Calculated by GISI) www.jifactor.com
ISSN Print: 0976-6308 and ISSN Online: 0976-6316
© IAEME Publication
MODELLING AND SIMULATION ON
VELOCITY AND PERMEABILITY TO
PREDICT BACILLUS ON LAG PHASE IN
PREDOMINANT LATERITIC AND SILTY
FORMATION IN COASTAL ABONNEMA,
NIGER DELTA OF NIGERIA
Eluozo. S. N
Subaka Nigeria Limited Port Harcourt Rivers State of Nigeria
Director and Principal Consultant Civil and Environmental Engineering,
Research and Development
Ode .T
Department of Civil Engineering, faculty of Engineering
Rivers State University of Science and Technology Port Harcourt
ABSTRACT
The deposition and migration process of bacillus lag phase condition has
been of paramount interest due it challenges in ground water quality, this
study mathematically analyze the migration process base on lag behaviour
the contaminant express in some formations, the study develop a model that
express the migration process and its behaviour between lateritic and silty
formation, the developed model simulated generated theoretical values, it has
shows the level of lag found to be insignificant as the rate of permeability
and velocity of flow influences the level of lag in the formation, the simulated
results were thoroughly compared with experimental values, both parameters
developed a faviourable fits, the validation of the developed model will
definitely made the developed concept a useful tools to experts.
Key words: Modelling and Simulation, Velocity and Permeability, Bacillus,
Lateritic and Silty Formation
Cite this Article: Asst. Prof. Abdul Ridah Saleh Al-Fatlawi and Ahmed Hadi
Hassan, CFRP Strengthening of Circular Concrete Slab with and without
Openings, International Journal of Civil Engineering and Technology, 7(1),
2016, pp. 304-314.
http://www.iaeme.com/IJCIET/issues.asp?JType=IJCIET&VType=7&IType=1
Modelling and Simulation on Velocity and Permeability to Predict Bacillus on Lag Phase in
Predominant Lateritic and Silty Formation in Coastal Abonnema, Niger Delta of Nigeria
http://www.iaeme.com/IJCIET/index.asp 305 editor@iaeme.com
1. INTRODUCTION
This travel time was assumed to cause sufficient die off of pathogenic bacteria from
contamination sources (Knorr, 1937). In the past decades, however, viruses, and more
recently protozoa like Cryptosporidium and Giardia, have been recognized as
pathogens of major concern in the water industry (Craun et al., 1997; MacKenzie et
al., 1994; Gerba et al., 1990). These organisms have been related to waterborne
diseases because of their persistence in the environment, resistance to water treatment,
and high infectivity. These organisms are different from bacteria in survival, surface
properties, and size. Moreover, it has become clear that die off in groundwater is not
the only process that governs the transport of microorganisms. For viruses it was
demonstrated that attachment to soil particles was more important than survival in the
groundwater (Schijven, 2001). Therefore, viruses and maybe protozoa could be
transported over longer distances in soil and thus be more significant to the microbial
safety of groundwater number of field studies have been carried out that established
either removal of indigenous microorganisms or lab-cultured seeded microorganisms
(Schijven et al. 1999, 2000, 2001; Van Olphen et al., 1993; Medema and Stuyvesant,
2002). These studies showed that soil passage poses a very effective barrier to
microorganisms, but critical situations may arise (Medema and Stuyfzand, 2002).
Such situations are intrusion of contaminations to unconfined aquifers above
groundwater wells, water abstraction during RBF from a gravel aquifer, with
increased risk during high flow events, or short circuiting during recollection in AR
systems. Field studies are valuable but hampered by some drawbacks. The
concentration of pathogens in the field is generally too low to assess removal, and
only non hazardous model micro-organisms (Escherichia coli, bacteriophage, and
spores of clostridia) can be used in spiking studies (Schijven et al., 2000).. The
importance of attachment and the surface properties of bacteriophage, bacteria, and
soil and of water quality parameters has been elucidated by column experiments
(Burge and Enkiri, 1978; Sobsey et al., 1980; Bales et al., 1991; Jin et al., 1997;
Goldschmid et al., 1972; Fletcher and Marshall, 1982; Scholl et al., 1990; McCaulou
et al., 1994). More recently, transport of the oocysts of Cryptosporidium in soil
columns was studied (Harter et al., 2001; Logan et al., 2001; Bradford and Bettahar,
2005; Tufenkji et al., 2004a), and results indicate the importance of straining on the
removal of these larger organisms. The significance of column studies increases when
results are related to field conditions of the selected soils and validated by field
studies, as described for phage MS2 in dune sand by Schijven (2001). Soil water
regime is highly affected by soil structure and its stability. Various soil structure types
may cause preferential flow or water immobilization (Kodešová et al., 2006, 2007,
2008). Soil structure breakdown may initiate a soil particle migration, formation of
less permeable or even impermeable layers and consequently decreased water fluxes
within the soil profile (Kodešová et al., 2009a). Soil aggregation is under control of
different mechanisms in different soil types and horizons (Kodešová et al., 2009b).
Soil structure and consequently soil hydraulic properties of tilled soil varied in space
and time (Strudley et al., 2008). The temporal variability of the soil aggregate stability
was shown for instance by Chan et al. (1994), and Yang and Wander (1998). While
Chan et al. (1994) documented that temporal changes of aggregate stability were not
positively related to living root length density; Yang and Wander (1998) suggested
that the higher aggregate stability was found due to crop roots, exudates microbial by-
products and wet/dry cycles. The temporal variability of the soil hydraulic properties
(mainly hydraulic conductivities, K) were investigated for instance in following
studies. Murphy et al. (1993) showed that K values at tensions of 10 and 40 mm
Eluozo. S. N and Ode .T
http://www.iaeme.com/IJCIET/index.asp 306 editor@iaeme.com
varied temporally due to the tillage, wetting/drying, and plant growth. Messing and
Jarvis (1993) presented that the K values decreased during the growing season due to
the structural breakdown by rain and surface sealing. Somaratne and Smettem (1993)
documented that while the K values at tension of 20 mm were reduced due to the
raindrop impact, the K values at tension of 40 mm were not influenced. Angulo-
Jaramillo et al. (1997) discovered that only the more homogeneous sandy soil under
furrow irrigation exhibited significant decrease in sorptivity. Petersen et al. (1997)
documented using the dye tracer experiment that cultivation reduced the number of
active preferential flow paths. Azevedo et al. (1998) measured tension infiltration
from 0 to 90 mm and showed that macropore flow decreased from 69% in July to
44% in September. Bodner et al. (2008) discussed the impact of the rainfall intensity,
soil drying and frost on the seasonal changes of soil hydraulic properties in the
structure-related range. Finally, Suwardji and Eberbach (1998) studied both,
aggregate stability and hydraulic conductivities. They documented the lowest
aggregate stability during the winter and increased in spring. The K values decreased
during the growing season. The goal of this study is to assess the seasonal variability
of the soil structure, aggregate stability and hydraulic properties with respect to each
other and to varying soil physical and chemical properties, soil management and
climatic conditions. (Veronika et al 2010).
2. DEVELOPED MATHEMATICAL MODEL
 
z
c
xDv
z
c
V
t
c








 (1)
Nomenclature
 = Porosity [ - ]
D(x) = Dispersion number [ - ]
V = Void Ratio [ - ]
 = Lag phase [- ]
C = Concentration [ML-3
]
Z = Depth [L ]
T = Time [T ]
v = Velocity [LT-1
]
)()(1
oCtCS
t
c



(2)
)()(1
oCzCS
z
c



(3)
)()(1
oCzCS
z
c



(4)
Modelling and Simulation on Velocity and Permeability to Predict Bacillus on Lag Phase in
Predominant Lateritic and Silty Formation in Coastal Abonnema, Niger Delta of Nigeria
http://www.iaeme.com/IJCIET/index.asp 307 editor@iaeme.com
Substituting equation (2), (3) and (4) into equation (1) yields:
   )()()()()( 111
oCzCSDvoCtCStCS   (5)
 )()()()( 111
zCDvSzVSCtCStCS   (6)
 )()()(1)( 11
zCDvSzCVStCStC  
(7)
 )()()(1)( 11
1 zDvCzCVStCS
S
tC  
(8)
1
)(
S
DvV
tC



(9)
(10)
11
)()()( DvCVtCtCStC   (11)
  )()( tCDvVoC   (12)
  )()(1
tCDvVtCS   (13)
DvV
tCS
tC



)(
)(
1
(14)
DvV
tS
tC



)(
)(
1
(15)
Furthermore, considering the boundary condition, we have at
0)()(0 1
 oCoCt
  0)()()()( 1
 zCDvzVCtCStC  (16)
0
0

 DvV
(17)
Considering the following boundary condition in the equation
)()()()()( 11
zCSVCozVCtSCotCSCotC  
)()( 11
zSCoDvzDvS  (18)
CoDvVCotSCtCtC   )()()( (19)
DvVtCtC  )()(
Eluozo. S. N and Ode .T
http://www.iaeme.com/IJCIET/index.asp 308 editor@iaeme.com
Considering the denominator in the equation, we have
 CoDvVtC  )( (20)
Considering



1
V
CoDvtC 

 

1
)(
(21)




 CoDv
tC
2
1
)(
(22)
  CoDvtC




1
1)( 2
(23)
  CoVtC   2
1)( (24)
)(tC (25)
  CoVDv  2
1 (26)
CoDvVVV   2
(27)
  02
  VVDvV (28)
Applying quadratic expression to equation (28), we have
  02
  VVDvV
a =
2
V , b = CoVDv and c = V
a
acbb
2
42


(29)






V
VVCoVDvCoVDv
2
42
(30)






V
VVCoVDvCoVDv
2
42
1
(31)






V
VVCoVDvCoVDv
2
42
2
(32)
Since we have stst
BA   it implies that





V
VVCoVDvCoVDv
ACt
2
4
exp
2
(33)
Modelling and Simulation on Velocity and Permeability to Predict Bacillus on Lag Phase in
Predominant Lateritic and Silty Formation in Coastal Abonnema, Niger Delta of Nigeria
http://www.iaeme.com/IJCIET/index.asp 309 editor@iaeme.com
If A = B = 1
t
V
VVCoVDvCoVDv
t
V
VVCoVDvCoVDv
tC


























 2
4
2
2
2
4
exp)( 
(34)
Applying inverse Laplace of the equation yield
  










 t
V
VVCoVDvCoVDv
CoCoDvttC


2
4
)(
2
t
V
VVCoVDvCoVDv
t
V
VVCoVDvCoVDv


































2
4
2
4 22
(35)






































V
VVCoVDvCoVDv
V
VVCoVDvCoVDv
Co
t
CoVDvtC
2
4
2
4
)(
22
2
t
V
VVCoVDvCoVDv
t
V
VVCoVDvCoVDv


























2
4
2
4 22

(36)
3. MATERIALS AND METHOD
Standard laboratory experiment where performed to monitor the rate of bacillus
concentration using column experiment at different formation, the soil deposition of
the strata were collected in sequences base on the structural deposition at different
locations, this samples collected at different location generate variation at different
depth producing different migration of bacillus concentration through its flow at
different strata, the experimental result are applied to be compared with the
theoretical values to determined the validation of the model.
Table 1 Theoretical values Bacillus Concentration of flow at Different Depths
Depth [M] Theoretical values.
3 9.84E-07
6 1.96E-06
9 2.95E-06
12 3.93E-06
15 2.46E-06
18 5.90E-06
21 6.90E-06
24 7.87E-06
27 8.85E-06
30 9.94E-06
33 1.08E-05
36 1.18E-05
Eluozo. S. N and Ode .T
http://www.iaeme.com/IJCIET/index.asp 310 editor@iaeme.com
Table 2 Comparison of Theoretical and Measured Values of Bacillus Concentration Different
Depth
Depth [M] Predicted values Measured Values
3 9.84E-07 9.77E-07
6 1.96E-06 1.88E-06
9 2.95E-06 2.88E-06
12 3.93E-06 3.77E-06
15 2.46E-06 2.33E-06
18 5.90E-06 5.88E-06
21 6.90E-06 6.77E-06
24 7.87E-06 7.67E-06
27 8.85E-06 8.78E-06
30 9.94E-06 9.89E-06
33 1.08E-05 1.04E-05
36 1.18E-05 1.14E-05
Table 3 Theoretical values of Bacillus Concentration at Different Depth
Time Per Day Theoretical values
10 7.68E-04
20 1.80E-03
30 3.10E-03
40 4.67E-03
50 6.50E-03
60 8.61E-03
70 1.10E-02
80 1.40E-02
90 1.70E-02
100 1.90E-02
110 2.30E-02
120 2.70E-02
Table 4 Comparison of Theoretical and Measured Values of Bacillus Concentration Different Time
Time Per Day Predicted Values Measured Values
10 7.68E-04 7.55E-04
20 1.80E-03 1.77E-03
30 3.10E-03 3.05E-03
40 4.67E-03 4.55E-03
50 6.50E-03 6.44E-03
60 8.61E-03 8.44E-03
70 1.10E-02 1.08E-02
80 1.40E-02 1.33E-02
90 1.70E-02 1.66E-02
100 1.90E-02 1.77E-02
110 2.30E-02 2.27E-02
120 2.70E-02 2.55E-02
Modelling and Simulation on Velocity and Permeability to Predict Bacillus on Lag Phase in
Predominant Lateritic and Silty Formation in Coastal Abonnema, Niger Delta of Nigeria
http://www.iaeme.com/IJCIET/index.asp 311 editor@iaeme.com
Figure1 Theoretical values of Bacillus Concentration at Different Time
Figure 2 Comparison of Theoretical and Measured Values of Bacillus Concentration
Different Depth
Figure3 Theoretical values of Bacillus Concentration at Different Time
0.00E+00
2.00E-06
4.00E-06
6.00E-06
8.00E-06
1.00E-05
1.20E-05
1.40E-05
0 10 20 30 40
Theoreticalvalues
Depth [m]
Theoretical values Ccnc
0.00E+00
2.00E-06
4.00E-06
6.00E-06
8.00E-06
1.00E-05
1.20E-05
1.40E-05
0 10 20 30 40
PredictedandMeasuredValues
Depth [m]
Predicted values Ccnc
Measured Values
0.00E+00
5.00E-03
1.00E-02
1.50E-02
2.00E-02
2.50E-02
3.00E-02
0 50 100 150
TheoreticalValues
Depth [m]
Theoretical values Ccnc
Eluozo. S. N and Ode .T
http://www.iaeme.com/IJCIET/index.asp 312 editor@iaeme.com
Figure 4 Comparison of Theoretical and Measured Values of Bacillus of Concentration
Different Depth
The study has express the behaviour of bacillus in its migration at different
condition, the migration process were observed to be in almost the same process in
the formation, these are base on the concentration of bacillus in formation, the
behaviour of bacillus from the graphical representation shows that exponential phase
of bacillus deposition were observed in the system, with slight fluctuation experienced
in both predicted and measured values, the study express lag phase of bacillus within
the lateritic soil formation, but migrated rapidly at were the silty formation were
deposited, the deposition of silty formation experiences higher degree of porosity in
such deltaic formation. The behaviour of the contaminant observed higher rate of
porosity in silty formation, the study has defined the influential output of porosity in
silty strata, and these condition has been observed to inhibit the lag phase condition of
bacillus in lateritic formation base on the structure of the lithology in deltaic
environment.
4. CONCLUSION
The deposition of bacillus expressing lag phase in some strata has been evaluated, the
condition of lateritic formation developing lag phase were found from the simulation
results, these reflect the reaction with other constituents that may have influences the
contaminant at lateritic formation to have developed lag phase in those strata, such
condition were to monitor various influences on the behaviour of the microbes at
different geological setting of the soil structure, the developed model has definitely
express the level of lag in the system , this study provide the platform which experts
can determined the rate of lag which has been found insignificant in the study location
from the simulation results, the study will be a useful tool in monitoring and
evaluation of bacillus contaminants in the study location.
0.00E+00
5.00E-03
1.00E-02
1.50E-02
2.00E-02
2.50E-02
3.00E-02
0 50 100 150
PredictedandMeasuredValues
Depth [M]
Predicted Values values
Measured Values
Modelling and Simulation on Velocity and Permeability to Predict Bacillus on Lag Phase in
Predominant Lateritic and Silty Formation in Coastal Abonnema, Niger Delta of Nigeria
http://www.iaeme.com/IJCIET/index.asp 313 editor@iaeme.com
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MODELLING AND SIMULATION ON VELOCITY AND PERMEABILITY TO PREDICT BACILLUS ON LAG PHASE IN PREDOMINANT LATERITIC AND SILTY FORMATION IN COASTAL ABONNEMA, NIGER DELTA OF NIGERIA

  • 1. http://www.iaeme.com/IJCIET/index.asp 304 editor@iaeme.com International Journal of Civil Engineering and Technology (IJCIET) Volume 7, Issue 1, Jan-Feb 2016, pp. 304-314, Article ID: IJCIET_07_01_025 Available online at http://www.iaeme.com/IJCIET/issues.asp?JType=IJCIET&VType=7&IType=1 Journal Impact Factor (2016): 9.7820 (Calculated by GISI) www.jifactor.com ISSN Print: 0976-6308 and ISSN Online: 0976-6316 © IAEME Publication MODELLING AND SIMULATION ON VELOCITY AND PERMEABILITY TO PREDICT BACILLUS ON LAG PHASE IN PREDOMINANT LATERITIC AND SILTY FORMATION IN COASTAL ABONNEMA, NIGER DELTA OF NIGERIA Eluozo. S. N Subaka Nigeria Limited Port Harcourt Rivers State of Nigeria Director and Principal Consultant Civil and Environmental Engineering, Research and Development Ode .T Department of Civil Engineering, faculty of Engineering Rivers State University of Science and Technology Port Harcourt ABSTRACT The deposition and migration process of bacillus lag phase condition has been of paramount interest due it challenges in ground water quality, this study mathematically analyze the migration process base on lag behaviour the contaminant express in some formations, the study develop a model that express the migration process and its behaviour between lateritic and silty formation, the developed model simulated generated theoretical values, it has shows the level of lag found to be insignificant as the rate of permeability and velocity of flow influences the level of lag in the formation, the simulated results were thoroughly compared with experimental values, both parameters developed a faviourable fits, the validation of the developed model will definitely made the developed concept a useful tools to experts. Key words: Modelling and Simulation, Velocity and Permeability, Bacillus, Lateritic and Silty Formation Cite this Article: Asst. Prof. Abdul Ridah Saleh Al-Fatlawi and Ahmed Hadi Hassan, CFRP Strengthening of Circular Concrete Slab with and without Openings, International Journal of Civil Engineering and Technology, 7(1), 2016, pp. 304-314. http://www.iaeme.com/IJCIET/issues.asp?JType=IJCIET&VType=7&IType=1
  • 2. Modelling and Simulation on Velocity and Permeability to Predict Bacillus on Lag Phase in Predominant Lateritic and Silty Formation in Coastal Abonnema, Niger Delta of Nigeria http://www.iaeme.com/IJCIET/index.asp 305 editor@iaeme.com 1. INTRODUCTION This travel time was assumed to cause sufficient die off of pathogenic bacteria from contamination sources (Knorr, 1937). In the past decades, however, viruses, and more recently protozoa like Cryptosporidium and Giardia, have been recognized as pathogens of major concern in the water industry (Craun et al., 1997; MacKenzie et al., 1994; Gerba et al., 1990). These organisms have been related to waterborne diseases because of their persistence in the environment, resistance to water treatment, and high infectivity. These organisms are different from bacteria in survival, surface properties, and size. Moreover, it has become clear that die off in groundwater is not the only process that governs the transport of microorganisms. For viruses it was demonstrated that attachment to soil particles was more important than survival in the groundwater (Schijven, 2001). Therefore, viruses and maybe protozoa could be transported over longer distances in soil and thus be more significant to the microbial safety of groundwater number of field studies have been carried out that established either removal of indigenous microorganisms or lab-cultured seeded microorganisms (Schijven et al. 1999, 2000, 2001; Van Olphen et al., 1993; Medema and Stuyvesant, 2002). These studies showed that soil passage poses a very effective barrier to microorganisms, but critical situations may arise (Medema and Stuyfzand, 2002). Such situations are intrusion of contaminations to unconfined aquifers above groundwater wells, water abstraction during RBF from a gravel aquifer, with increased risk during high flow events, or short circuiting during recollection in AR systems. Field studies are valuable but hampered by some drawbacks. The concentration of pathogens in the field is generally too low to assess removal, and only non hazardous model micro-organisms (Escherichia coli, bacteriophage, and spores of clostridia) can be used in spiking studies (Schijven et al., 2000).. The importance of attachment and the surface properties of bacteriophage, bacteria, and soil and of water quality parameters has been elucidated by column experiments (Burge and Enkiri, 1978; Sobsey et al., 1980; Bales et al., 1991; Jin et al., 1997; Goldschmid et al., 1972; Fletcher and Marshall, 1982; Scholl et al., 1990; McCaulou et al., 1994). More recently, transport of the oocysts of Cryptosporidium in soil columns was studied (Harter et al., 2001; Logan et al., 2001; Bradford and Bettahar, 2005; Tufenkji et al., 2004a), and results indicate the importance of straining on the removal of these larger organisms. The significance of column studies increases when results are related to field conditions of the selected soils and validated by field studies, as described for phage MS2 in dune sand by Schijven (2001). Soil water regime is highly affected by soil structure and its stability. Various soil structure types may cause preferential flow or water immobilization (Kodešová et al., 2006, 2007, 2008). Soil structure breakdown may initiate a soil particle migration, formation of less permeable or even impermeable layers and consequently decreased water fluxes within the soil profile (Kodešová et al., 2009a). Soil aggregation is under control of different mechanisms in different soil types and horizons (Kodešová et al., 2009b). Soil structure and consequently soil hydraulic properties of tilled soil varied in space and time (Strudley et al., 2008). The temporal variability of the soil aggregate stability was shown for instance by Chan et al. (1994), and Yang and Wander (1998). While Chan et al. (1994) documented that temporal changes of aggregate stability were not positively related to living root length density; Yang and Wander (1998) suggested that the higher aggregate stability was found due to crop roots, exudates microbial by- products and wet/dry cycles. The temporal variability of the soil hydraulic properties (mainly hydraulic conductivities, K) were investigated for instance in following studies. Murphy et al. (1993) showed that K values at tensions of 10 and 40 mm
  • 3. Eluozo. S. N and Ode .T http://www.iaeme.com/IJCIET/index.asp 306 editor@iaeme.com varied temporally due to the tillage, wetting/drying, and plant growth. Messing and Jarvis (1993) presented that the K values decreased during the growing season due to the structural breakdown by rain and surface sealing. Somaratne and Smettem (1993) documented that while the K values at tension of 20 mm were reduced due to the raindrop impact, the K values at tension of 40 mm were not influenced. Angulo- Jaramillo et al. (1997) discovered that only the more homogeneous sandy soil under furrow irrigation exhibited significant decrease in sorptivity. Petersen et al. (1997) documented using the dye tracer experiment that cultivation reduced the number of active preferential flow paths. Azevedo et al. (1998) measured tension infiltration from 0 to 90 mm and showed that macropore flow decreased from 69% in July to 44% in September. Bodner et al. (2008) discussed the impact of the rainfall intensity, soil drying and frost on the seasonal changes of soil hydraulic properties in the structure-related range. Finally, Suwardji and Eberbach (1998) studied both, aggregate stability and hydraulic conductivities. They documented the lowest aggregate stability during the winter and increased in spring. The K values decreased during the growing season. The goal of this study is to assess the seasonal variability of the soil structure, aggregate stability and hydraulic properties with respect to each other and to varying soil physical and chemical properties, soil management and climatic conditions. (Veronika et al 2010). 2. DEVELOPED MATHEMATICAL MODEL   z c xDv z c V t c          (1) Nomenclature  = Porosity [ - ] D(x) = Dispersion number [ - ] V = Void Ratio [ - ]  = Lag phase [- ] C = Concentration [ML-3 ] Z = Depth [L ] T = Time [T ] v = Velocity [LT-1 ] )()(1 oCtCS t c    (2) )()(1 oCzCS z c    (3) )()(1 oCzCS z c    (4)
  • 4. Modelling and Simulation on Velocity and Permeability to Predict Bacillus on Lag Phase in Predominant Lateritic and Silty Formation in Coastal Abonnema, Niger Delta of Nigeria http://www.iaeme.com/IJCIET/index.asp 307 editor@iaeme.com Substituting equation (2), (3) and (4) into equation (1) yields:    )()()()()( 111 oCzCSDvoCtCStCS   (5)  )()()()( 111 zCDvSzVSCtCStCS   (6)  )()()(1)( 11 zCDvSzCVStCStC   (7)  )()()(1)( 11 1 zDvCzCVStCS S tC   (8) 1 )( S DvV tC    (9) (10) 11 )()()( DvCVtCtCStC   (11)   )()( tCDvVoC   (12)   )()(1 tCDvVtCS   (13) DvV tCS tC    )( )( 1 (14) DvV tS tC    )( )( 1 (15) Furthermore, considering the boundary condition, we have at 0)()(0 1  oCoCt   0)()()()( 1  zCDvzVCtCStC  (16) 0 0   DvV (17) Considering the following boundary condition in the equation )()()()()( 11 zCSVCozVCtSCotCSCotC   )()( 11 zSCoDvzDvS  (18) CoDvVCotSCtCtC   )()()( (19) DvVtCtC  )()(
  • 5. Eluozo. S. N and Ode .T http://www.iaeme.com/IJCIET/index.asp 308 editor@iaeme.com Considering the denominator in the equation, we have  CoDvVtC  )( (20) Considering    1 V CoDvtC      1 )( (21)      CoDv tC 2 1 )( (22)   CoDvtC     1 1)( 2 (23)   CoVtC   2 1)( (24) )(tC (25)   CoVDv  2 1 (26) CoDvVVV   2 (27)   02   VVDvV (28) Applying quadratic expression to equation (28), we have   02   VVDvV a = 2 V , b = CoVDv and c = V a acbb 2 42   (29)       V VVCoVDvCoVDv 2 42 (30)       V VVCoVDvCoVDv 2 42 1 (31)       V VVCoVDvCoVDv 2 42 2 (32) Since we have stst BA   it implies that      V VVCoVDvCoVDv ACt 2 4 exp 2 (33)
  • 6. Modelling and Simulation on Velocity and Permeability to Predict Bacillus on Lag Phase in Predominant Lateritic and Silty Formation in Coastal Abonnema, Niger Delta of Nigeria http://www.iaeme.com/IJCIET/index.asp 309 editor@iaeme.com If A = B = 1 t V VVCoVDvCoVDv t V VVCoVDvCoVDv tC                            2 4 2 2 2 4 exp)(  (34) Applying inverse Laplace of the equation yield               t V VVCoVDvCoVDv CoCoDvttC   2 4 )( 2 t V VVCoVDvCoVDv t V VVCoVDvCoVDv                                   2 4 2 4 22 (35)                                       V VVCoVDvCoVDv V VVCoVDvCoVDv Co t CoVDvtC 2 4 2 4 )( 22 2 t V VVCoVDvCoVDv t V VVCoVDvCoVDv                           2 4 2 4 22  (36) 3. MATERIALS AND METHOD Standard laboratory experiment where performed to monitor the rate of bacillus concentration using column experiment at different formation, the soil deposition of the strata were collected in sequences base on the structural deposition at different locations, this samples collected at different location generate variation at different depth producing different migration of bacillus concentration through its flow at different strata, the experimental result are applied to be compared with the theoretical values to determined the validation of the model. Table 1 Theoretical values Bacillus Concentration of flow at Different Depths Depth [M] Theoretical values. 3 9.84E-07 6 1.96E-06 9 2.95E-06 12 3.93E-06 15 2.46E-06 18 5.90E-06 21 6.90E-06 24 7.87E-06 27 8.85E-06 30 9.94E-06 33 1.08E-05 36 1.18E-05
  • 7. Eluozo. S. N and Ode .T http://www.iaeme.com/IJCIET/index.asp 310 editor@iaeme.com Table 2 Comparison of Theoretical and Measured Values of Bacillus Concentration Different Depth Depth [M] Predicted values Measured Values 3 9.84E-07 9.77E-07 6 1.96E-06 1.88E-06 9 2.95E-06 2.88E-06 12 3.93E-06 3.77E-06 15 2.46E-06 2.33E-06 18 5.90E-06 5.88E-06 21 6.90E-06 6.77E-06 24 7.87E-06 7.67E-06 27 8.85E-06 8.78E-06 30 9.94E-06 9.89E-06 33 1.08E-05 1.04E-05 36 1.18E-05 1.14E-05 Table 3 Theoretical values of Bacillus Concentration at Different Depth Time Per Day Theoretical values 10 7.68E-04 20 1.80E-03 30 3.10E-03 40 4.67E-03 50 6.50E-03 60 8.61E-03 70 1.10E-02 80 1.40E-02 90 1.70E-02 100 1.90E-02 110 2.30E-02 120 2.70E-02 Table 4 Comparison of Theoretical and Measured Values of Bacillus Concentration Different Time Time Per Day Predicted Values Measured Values 10 7.68E-04 7.55E-04 20 1.80E-03 1.77E-03 30 3.10E-03 3.05E-03 40 4.67E-03 4.55E-03 50 6.50E-03 6.44E-03 60 8.61E-03 8.44E-03 70 1.10E-02 1.08E-02 80 1.40E-02 1.33E-02 90 1.70E-02 1.66E-02 100 1.90E-02 1.77E-02 110 2.30E-02 2.27E-02 120 2.70E-02 2.55E-02
  • 8. Modelling and Simulation on Velocity and Permeability to Predict Bacillus on Lag Phase in Predominant Lateritic and Silty Formation in Coastal Abonnema, Niger Delta of Nigeria http://www.iaeme.com/IJCIET/index.asp 311 editor@iaeme.com Figure1 Theoretical values of Bacillus Concentration at Different Time Figure 2 Comparison of Theoretical and Measured Values of Bacillus Concentration Different Depth Figure3 Theoretical values of Bacillus Concentration at Different Time 0.00E+00 2.00E-06 4.00E-06 6.00E-06 8.00E-06 1.00E-05 1.20E-05 1.40E-05 0 10 20 30 40 Theoreticalvalues Depth [m] Theoretical values Ccnc 0.00E+00 2.00E-06 4.00E-06 6.00E-06 8.00E-06 1.00E-05 1.20E-05 1.40E-05 0 10 20 30 40 PredictedandMeasuredValues Depth [m] Predicted values Ccnc Measured Values 0.00E+00 5.00E-03 1.00E-02 1.50E-02 2.00E-02 2.50E-02 3.00E-02 0 50 100 150 TheoreticalValues Depth [m] Theoretical values Ccnc
  • 9. Eluozo. S. N and Ode .T http://www.iaeme.com/IJCIET/index.asp 312 editor@iaeme.com Figure 4 Comparison of Theoretical and Measured Values of Bacillus of Concentration Different Depth The study has express the behaviour of bacillus in its migration at different condition, the migration process were observed to be in almost the same process in the formation, these are base on the concentration of bacillus in formation, the behaviour of bacillus from the graphical representation shows that exponential phase of bacillus deposition were observed in the system, with slight fluctuation experienced in both predicted and measured values, the study express lag phase of bacillus within the lateritic soil formation, but migrated rapidly at were the silty formation were deposited, the deposition of silty formation experiences higher degree of porosity in such deltaic formation. The behaviour of the contaminant observed higher rate of porosity in silty formation, the study has defined the influential output of porosity in silty strata, and these condition has been observed to inhibit the lag phase condition of bacillus in lateritic formation base on the structure of the lithology in deltaic environment. 4. CONCLUSION The deposition of bacillus expressing lag phase in some strata has been evaluated, the condition of lateritic formation developing lag phase were found from the simulation results, these reflect the reaction with other constituents that may have influences the contaminant at lateritic formation to have developed lag phase in those strata, such condition were to monitor various influences on the behaviour of the microbes at different geological setting of the soil structure, the developed model has definitely express the level of lag in the system , this study provide the platform which experts can determined the rate of lag which has been found insignificant in the study location from the simulation results, the study will be a useful tool in monitoring and evaluation of bacillus contaminants in the study location. 0.00E+00 5.00E-03 1.00E-02 1.50E-02 2.00E-02 2.50E-02 3.00E-02 0 50 100 150 PredictedandMeasuredValues Depth [M] Predicted Values values Measured Values
  • 10. Modelling and Simulation on Velocity and Permeability to Predict Bacillus on Lag Phase in Predominant Lateritic and Silty Formation in Coastal Abonnema, Niger Delta of Nigeria http://www.iaeme.com/IJCIET/index.asp 313 editor@iaeme.com REFERENCES [1] Angulo-Jaramillo R, Moreno F, Clothier BE, Thony JL, Vachaud G, Fernandez- Boy E, Cayuela JA B(1997)Seasonal variation of hydraulic properties of soils measured using a tension disc infiltrometer. Soil Science Society of America Journal 61, 27-32 [2] Bodner G, Loiskandl W, Buchan G, Kaul HP (2008) Natural and management- induced dynamics of hydraulic conductivity along a cover-cropped field slope. Geoderma 146, 317-325. [3] Burge, W. D., and N. K. Enkiri. 1978. Virus adsorption in five soils. J. EnvironQual. 7:73-76 [4] [4] Bales, R. C., S. R. Hinkle, T. W. Kroeger, and K. Stocking. 1991. Bacteriophage adsorption during transport through porous media: chemical perturbations and reversibility. Environ. Sci. Technol. 25:2088-2095 [5] Chan KY, Heenan DP, Ashley R (1994) Seasonal changes in surface aggregate stability under different tillage and crops. Soil and Tillage Research 28, 301-314. [6] Jin, Y., M. V. Yates, S. S. Thompson, and W. A. Jury. 1997. Sorption of viruses during flow through saturated sand columns. Environ. Sci. Technol. 31:548-555. [7] Knorr, N. 1937. Die Schutzzonenfrage in der Trinkwater-hygiene. Das Gas- und Wasserfach 80:330-355. [8] Goldschmid, J., D. Zohar, J. Argaman, and Y. Kott. 1972. Effect of dissolved salts on the filtration of coliform bacteria in sand dunes. In P. Jenkins (ed.), Advances in water pollution research. Pergamon Press, Oxford, UK. [9] Bradford, S. A., and M. Bettahar. 2005. Straining, attachment and detachment of Cryptosporidium oocysts in saturated porous media. J. Environ. Qual.4:469-478. [10] Gerba, C. P., and J. B. Rose. 1990. Viruses in source and drinking water. In G.A. McFeters (ed.) 'Drinking water Microbiology: progress and recent developments', Springer-Verlag New-York Inc [11] Craun, G. F., P. S. Berger, and R. L. Calderon. 1997. Coliform bacteria and waterborne disease outbreaks. J. Am. Water Work Assoc. 89:96-104 [12] Medema, G. J., M. Bahar, and F. M. Schets. 1997. Survival of Cryptosporidium parvum, Escherichia coli, faecal streptococci and Clostridium perfringens in river water. Wat. Sci. Tech. 35:249-252. [13] MacKenzie, W. R. H., N.J. , M. E. Proctor, S. Gradus, K. A. Blair, D. E. Peterson, J. J. Kazmierczak, D. G. Addiss, K. R. Fox, J. B. Rose, and J. P. Davis. 1994. A massive outbreak in Milwaukee of Cryptosporidium infection transmitted through the public water supply. New. Engl. J. Med. 331:161-167. [14] Schijven, J. F., W. Hoogenboezem, S. M. Hassanizadeh, and J. H. Peters. 1999. Modelling removal of bacteriophage MS2 and PRD1 by dune recharge at Castricum, Netherlands. Water Resour. Res. 35:1101-1111. [15] Schijven, J. F., and S. M. Hassanizadeh. 2000. Removal of viruses by soil passage: overview of modeling, processes and parameters. Crit. Rev. Envrion. Sci. Tech. 31:49-125. [16] Schijven, J. F. 2001. Virus removal from groundwater by soil passage. TechnischeUniversiteit Delft, Delft, the Netherlands. [17] Logan, J. L., T. K. Stevik, R. L. Siegrist, and R. M. Ronn. 2001. Transport and fate of Cryptosporidium parvum oocysts in intermittent sand filters. Water Res. 35:4359-4369. [18] Fletcher, M., and K. C. Marshall. 1982. Are solid surfaces of ecological significance to aquatic bacteria. Adv. Microb. Ecol. 6:199-236.
  • 11. Eluozo. S. N and Ode .T http://www.iaeme.com/IJCIET/index.asp 314 editor@iaeme.com [19] Harter, T., S. Wagner, and E. R. Atwill. 2001. Colloid transport and filtration of Cryptosporidium in sandy soils and aquifer sediments. Environ. Sci. Technol. 34:62-70. [20] Medema, G. J., and P. J. Stuyfzand. 2002. Presented at the 4th international symposium on artificial recharge, Adelaide, Australia, September 22-26. [21] Kodešová R, Kodeš V, Žigová A, Šimunek J (2006) Impact of plant roots and soil organisms on soil micromorphology and hydraulic properties. Biologia 61, S339–S343. [22] Kodešová R, Kocárek M, Kodeš V, Šimunek J, Kozák J (2008) Impact of soil Micromorphological features on water flow and herbicide transport in soils. Vadose Zone Journal 7, 798–809 [23] Kodešová R, Vignozzi N, Rohošková M, Hájková T, Kocárek M, Pagliai M, Kozák J, Šimunek J (2009a) Impact of varying soil structure on transport processes in different diagnostic horizons of three soil types, Journal of Contaminant Hydrology 104, 107-125. [24] Kodešová R, Rohošková M, Žigová A (2009b) Comparison of aggregate stability within six soil profiles under conventional tillage using various laboratory tests. Biologia 64, 550-554. [25] Messing I, Jarvis NJ (1993) Temporal variation in the hydraulic conductivity of a tiled clay soil as measured by tension infiltrometer. Journal of Soil Science 44, 11-24. [26] Somaratne NM, Smettem KRJ (1993) Effect of cultivation and raindrop impact on the surface hydraulic properties of an alfisol under wheat. Soil and Tillage Research 26, 115-125. [27] Strudley WM, Green TR, Ascough II JC (2008) Tillage effects on soil hydraulic properties in space and time: State of the science. Soil and Tillage Research 99, 4-48. [28] Yang XM, Wander MM (1998) Temporal changes in dry aggregate size and stability. Soil and Tillage Research 49, 173-183 [29] VeronikaJirkuA, RadkaKodešováA, Marcela MühlhanselováA and Anna Žigová B 2010 Seasonal variability of soil structure and soil hydraulic properties World Congress of Soil Science, Soil Solutions for a Changing World 1 6 August 2010, Brisbane, Australia. Published on DVD. [30] Eluozo, S. N. 2013, Mathematical model on inverse migration of enteromobacter in homogeneous coarse sand column in coastal area of port Harcourt, Niger delta environment International Journal of Sustainable Energy and Environment Vol. 1, No. 3, PP: 56 – 67. [31] S.O. Nkakini and Ndor .M.Vurasi, Ergonomic Evaluation of Lawn Mower Operation for Comfort in Rivers State, Nigeria. International Journal of Advanced Research in Engineering and Technology, 6(7), 2015, pp. 43-51 [32] Eluozo. S. N and Ode T, Mathematical Model to Monitor Stiff Clay Compression Index in Wet Land Area of Degema. International Journal of Advanced Research in Engineering and Technology, 6(12), 2015, pp. 59-72. [33] Eluozo. S. N and Ode T, Modeling and Simulation of Compression Strength for Firm Clay in Swampy Area of Ahoada East. International Journal of Advanced Research in Engineering and Technology, 6(12), 2015, pp. 73-85.