dc.description.abstract |
Groundwater is considered as the major source to meet the requirements of various demands, such
as agricultural, domestic and industrial use. The movement of groundwater is slower as compared
to the surface water which makes it more susceptible to pollution. Solute (contaminant) transport
through soil (porous media) has been an important area of research for decades in the field of geoenvironmental engineering. There are numerous sources that can contaminate soil and
groundwater e.g. migration of leachate from dumping site, release of chemicals from mining
operations such as tailing ponds. Contaminants when released into the environment, their transport
occurs in the saturated groundwater zone as they infiltrate beyond the vadose zone. These
contaminants cause pollution by interacting with water and soil at physical, chemical and
hydrological domains. Thus, it becomes important to understand the transport mechanism of solute
through saturated porous media so that the health risk can be avoided by detecting, simulating and
predicting the movement of contaminant along with the groundwater. Solute transport in soil and
groundwater is governed by various physical, chemical and biological process that takes place
between solute and porous media. Advective transport with the flowing groundwater, mechanical
dispersion due to heterogeneity of porous media, molecular diffusion, decay processes and
equilibrium and non-equilibrium solute exchange with the solid phase are some of the well-known
processes which govern the solute transport through porous media. All these processes play an
important role in plume spreading and dilution, therefore quantification of impact of these
processes on solute transport is essential to ensure the optimal cleaning operations. Most
challenging task is to accurately predict the arrival time and spatial patterns of contaminant plume
in the subsurface environment. The difficulty in prediction increases with the heterogeneity and
chemical properties of solute and porous media. When solute transport parameters are different at
different spatial and temporal scale, then predicting the behavior of solute in porous media become
difficult.
There are numerous studies that utilize numerical modelling technique to study the contaminant
behaviour in heterogeneous porous media. It has been reported in literature that the dispersion
phenomenon affects the plume behaviour in porous media. Influence of scale (distance) - or timedependent dispersion on solute transport has been observed at various scales. Therefore, present
study focuses on the development of solute transport model which incorporate time-dependent
dispersion with physical partitioning of heterogeneous porous media. Physical non-equilibrium is
accounted by diffusive mass transfer between mobile and immobile regions partitioning within the
porous medium.
In this study, hybrid numerical solution of the mobile-immobile model (MIM) with linear and
asymptotic time-dependent dispersion has been presented to account for heterogeneity of porous
media. Observed data of solute transport through heterogeneous porous media (heterogeneous soil
column and hydraulically coupled stratified porous media) has been simulated using constant,
linear and asymptotic time-dependent dispersion models. To compare the simulation capabilities
of transport models, results of timescale breakthrough curves and temporal moments have been
compared between constant and time-dependent dispersion models.
Analysis of simulated breakthrough curves suggested that the system is under the strong influence
of physical nonequilibrium which is evident by variable mass transfer coefficient estimated at
different down-gradient distances. Non-Gaussian breakthrough curves comprising long tails are
simulated well with the MIM incorporating asymptotic time-dependent dispersion model.
Asymptotic dispersion function is found to be capable of capturing the rising limb of the solution
phase breakthrough curves with improved accuracy, whereas tailing part simulation capabilities
were similar for both asymptotic and linear time-dependent dispersion functions.
Further, the study deals with the estimation of solute transport parameters in saturated porous
media with time-dependent dispersion models. Inverse parameter estimation procedure has been
developed by coupling finite difference based solute transport model with the LevenbergMarquardt algorithm. It is observed that the optimization algorithm results in non-unique optimal
estimates for the case of more than three unknown parameter estimation with asymptotic timedependent dispersion model. Asymptotic time-dependent dispersion model results in less number
of non-unique optimal estimate parameters combinations in comparison to linear time-dependent
dispersion model. Optimization algorithm resulted in non-unique estimates for asymptotic
dispersion model in the case of simultaneous estimation of two or more unknown parameters. This
is due to presence of equilibrium sorption coefficients of mobile and immobile region. Finally,
inverse algorithm is utilized to estimate unknown transport parameters from a column experiment
data of conservative solute and it is concluded that the asymptotic time-dependent dispersion
model fits the observed data much better than linear time-dependent dispersion model.
In the end, temporal moment analysis is presented to study solute plume behavior and sensitivity
of time-dependent transport parameters. Temporal moment analysis revealed that the solute mass
recovery, mean residence time and variance of breakthrough curve are sensitive to the estimated
parameters. It also revealed the limitation of MIML at higher travel distances and endorsed the use
of MIMA for field applications due to its realistic representation of spreading, skewness and mean
travel time of solute plume. Zeroth temporal moment for MIMA model attains an asymptotic value
as the plume travel distance increases within porous medium while for MIML it keeps on
decreasing. The pattern of the first moment reveals the physical ever-growing nature of the MIML
model which tends to demonstrate nonrealistic representation of the plume behavior without any
upper bound. It can be concluded from the study that MIM with asymptotic time-dependent
dispersion function is a simpler yet powerful tool to account for medium's heterogeneity. |
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