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Inference Network in
Environmental Mapping

Anshu Gupta
Centre for Remote Sensing & GIS,
NIT, Bhopal, India
anshugupta20002001@gmail.com

Vivek Dey
Civil Engineering Department,
Indian Institute of Technology,
Kanpur, India
vivekde@gmail.com
Alok Choudhary
Head of Image Processing, M.P.
Council of Science & Technology,
Bhopal, India
alok@yahoo.com

Fig. 1: Location of wards under the study
Environmental quality
assessment is essential
for urban development.
Rapid urbanisation has made it
all the more essential now than
before. But there is dearth of
appropriate techniques to assess
urban environment quality
(UEQA). Here is a technique that
is feasible, flexible and valid.
UEQA requires environmental information
in the form of air quality, noise
quality, topography
as slope and
aspect, vegetation
quantity
and quality of
greenness,
water quality,
soil quality etc.
This work deals
only with the
first four qualities.
Environmental
information has
the obvious spatial
character
that can be
addressed by
geographical
information system
(GIS). For
example, air
quality may
vary for different land-use classes. Population
density, as a socio-economic
factor involved in urban environmental
quality evaluation (UEQE), also
changes in the different spatial unit.
Other environmental factors such as
noise and green coverage also have
spatial character. So, while evaluating
the UEQ, GIS provides a powerful tool
to represent environmental information
in support of environmental evaluation
(Dai, Lee et al. 2001). An important
feature of GIS is its ability to generate
new information by integrating
diverse datasets. The purpose of environmental
evaluation in this study is
to represent environmental quality in
the form of maps which combines all
information of each of the environmental
factors.
STUDY AREA
Bhopal, the capital of Madhya Pradesh,
is one of the fastest growing cities of
India (Bhopal City Development Plan
under JNNURM). The city, also known
as "the city of lakes", is losing its beauty
under the increasing pressures of
urbanisation.
DATA AND MATERIAL
Spatial Data: Remote sensing satellite
data used are - CARTOSAT- 1 PAN (2.5 m
resolution) of Bhopal municipal corporation
area, dated January 2007 and IRS
P-6 LISS IV MX (5.8 m resolution) of
Bhopal municipal corporation area,
dated January 2007. High resolution
images (2.5 m) provide more details
about the spatial features. However,
multispectral images provide more
land cover information than panchromatic
images, as each spectral waveband
provides specific information
about land cover features. Fusion of
multispectral and high spatial resolution
panchromatic data enhances the
understanding of both spatial and
spectral resolution of the feature and
also enhances the accuracy and visual
interpretation (Jensen J. R.). Annual
mean concentration levels of air and
noise pollution (ward wise and along
four major traffic corridors) for the year
2006 have been collected from Madhya
Pradesh State Pollution Control Board,
LEA Associates South Asian Pvt. Ltd.
and Egis BCEOM India Pvt. Ltd. Data
obtained pertain to spatially well distributed
locations. These locations are
considered as sample locations and
data of the complete area was obtained
by spatial interpolation IDW using GIS.
METHODOLOGY
Environmental information for UEQE
assessment is broken into smaller components
or indicators. Air quality, noise
quality, topography, slope and aspects,
vegetation as NDVI, demography of the
study area and land use have been
evaluated as per their contribution
towards urban environmental pollution
(UEP). The contribution of traffic
has been given a special attention in
evaluating UEP. Road buffer (Kwang
Hoon Chi, No-Wook Park, 2002) has
been created along major traffic corridors
to consider the enhanced effect of
traffic towards air and noise pollution.
Each of the smaller components has
been shown at the topmost level in Figure
2. The combination of indicators
was carried out using the analytical
hierarchical process and fuzzy weights
which involves the opinion of experts
in urban pollution board, urban development,
meteorology and urban road
and traffic development (John M., Martin
Hale (2001)). Fuzzy inference network
has been established as shown in
Figure 2 to incorporate all the environmental
information in a logical manner.
Boolean inference network is similar
but the difference lies in the combination
strategy.
Instead of fuzzy
weights, Boolean
weights of 0 and 1
are considered and
Boolean algebraic
sum and Boolean
OR are used to
evaluate the final
quality map (Figure
4). Threshold for the four evaluation
classes is determined by trial and error.
Exact classes of few of the locations,
used to evaluate interpolated data, are
evaluated by experts. Threshold, which
classifies the training location correctly
with maximum accuracy, is chosen as
threshold for both the Boolean and
fuzzy approach.

Fig. 2: Fuzzy Inference Network
Each component's effect in enhancing
urban environmental pollution is evaluated
in a spatial raster layer format
through GIS. Considering the raster
data structure, every indicator is considered
as the individual layer in the
fuzzy overlay operation. The value of
each cell is the score of the indicator
considered (Chi, Park and Chung, 2002).
The implementation process of fuzzy
multi-criteria evaluation in GIS
through fuzzy inference network
includes three phases. Firstly, every
bottom indicator of each component is
overlaid based on fuzzy operation, also
called intermediate hypothesis. For
example, in air pollution criteria, the
criterion consists of four indicators
(SO2, NO2, SPM and CO) in wards as
well as along the four major traffic corridors.
The first phase of evaluation is
to overlay these four indicators based
on fuzzy operation (fuzzy algebraic
sum). That is to say, it is a bottom to top
approach. Secondly, the fuzzy operation
is carried out to overlay air pollution
in wards and air pollution along
road (Fuzzy OR). Finally, the final

Table 1: Area Distribution
hypothesis performing the fuzzy overlay
operation of environment pollution
and physical environment component
to get the final quality map (fuzzy
GAMMA). 'GAMMA' operator has been
used while applying FUZZY LOGIC technique
to obtain the final output map.
FUZZY ALGEBRAIC SUM and FUZZY OR
are used as intermediate hypothesis.
The final criteria map by BOOLEAN theory
has been processed by using
"ARITHMETIC SUM". The results so
obtained have been classified under
four categories of pollution. These evaluation
classes are Low, Moderate, High
and Critical.

(Fig. 3: Classified Final Quality Map by Fuzzy Approach) (Fig. 4: Final Quality Map by Conventional Approach)
DISCUSSION AND
ANALYSIS
The major difference between the two
maps is on the roadside pollution. From
the map using fuzzy approach, it is
clearly seen that the areas along the
major traffic corridors are in 'cyan',
indicating that these areas are highly
polluted. This is not at all seen in the
map using conventional approach.
With Fuzzy approach, the information
on pollution is retained and clearly
reflected in the evaluation result for
environmental pollution, whereas this
information is lost with the conventional
(Boolean) approach during the
process of evaluation. This is because
the fuzzy approach employs a set of
logically evaluated weights to determine
in what degree the component
belongs to one evaluation class.

Table 2: Study Area Covered in Each Class
Ambiguity resolution
is more in
fuzzy approach
because of the
continuous range
of values whereas
in Boolean
approach, it is a
discrete integer
value. This clearly
suggests that fuzzy approach will give
more information about the pollution
level than the Boolean approach which
is also evident from the higher percentage
of area obtained by fuzzy approach
in critical class.
VALIDATION
Validation of the obtained results is
carried out by a field visit to a sample
location other than the sample locations
used for map evaluation. Urban
environmental quality at this sample
location is evaluated by the panel of
experts from urban pollution board,
urban development, meteorology and
urban road and traffic development.
Some of the major anomalies in
Boolean and fuzzy results are illustrated
along with the reasons behind the
results.

Fig. 5: Pollution along major roads
As encircled in Figure 6, the area
labelled as A (Karariya Sajidabad),
shows different behaviour in fuzzy and
Boolean approach. The anomaly in the
observed area is that Boolean approach
is showing the area in the High zone
while Fuzzy approach categorises it in
Low and Moderate class. The reason for
the above difference is the land use.
Upon a field visit to the area, agricultural
farms (vegetation) are found. The difference
is also obtained around the area
shown in the rectangular box B (Nakkar
Khana). Now observe the area covered
under rectangle 'B'. The area has well
structured road network (VVIP road)
due to which the traffic runs smoothly.
But after just around 0.5 - 1.0 km, the
area, Peer Gate, comes in Critical class.

Fig. 6: Critical Condition in Old City of Bhopal
The Boolean approach is highly influenced
by this area and shows the area
around VVIP road in critical class where
as in fuzzy approach, the quality of
environment decreases gradually from
high to critical class which reveals the
continuous behaviour of fuzzy
approach.
CONCLUSION
Inference network provides a flexible
format in which at every stage, any
new component can be added to the
network while continuing to maintain
the logical format.
Evaluated final quality map with the
available data has established the feasibility
of the inference network in
urban environmental quality assessment.
Further, the integration of fuzzy
logic and GIS through inference network
in evaluating urban environmental
quality gives better results than the
Boolean approach. The ability of fuzzy
approach to quantify the ambiguity of
complexity of urban environmental
quality has been established on comparison
with the Boolean approach by
using the error matrix.
Error matrix shows the overall accuracy
of 55 % of Boolean approach with
respect to the fuzzy approach. This concludes
that conventional Boolean
approach is insufficient in explaining
the urban environmental quality.