ENVIRONMENTAL CONSEQUENCES OF INDUSTRIAL DEVELOPMENT -A CASE STUDY OF AND DISTRICTS

ABSTRACT

THESIS SUBMITTED TO ALIGARH MUSLIM UNIVERSITY FOR THE AWARD OF THE DEGREE OF ©ottor of pjjilostopljp IN GEOGRAPHY

BY NIGAR ANJUM

UNDER THE SUPERVISION OF PROF. M. FAROOQ SIDDIQI

DEPARTMENT OF GEOGRAPHY ALIGARH MUSLIM UNIVERSITY ALIGARH () 1995 ABSTRACT

India, being a developing country is striving its best for rapid development of industry, agriculture, science and technology, means of transport and communication. However, associated with developmental activity, the problem of environmental pollution inevitably poses a threat to human survival. It is true that any developing country can prosper only with industrialisation and more so far India where they have also in solving the unemployment problem created by rapid growth of population but as a side effect they lead to environmental pollution to such an extent that life of the people is affected in various ways.

Maintenance of purity and safety of the environment in the face of increasing urbanisation, industrialisation and mechanisation of daily life has thus become a challenging task. In the interest of the present and future generation, necessary steps should be undertaken to make sustainable use of land, its mineral and water resources, plant and animals so that the purity of air water and land may be preserved, reproduction of natural wealth may be ensured and quality of environment may be improved. 2

The study area lies between 28°29' and 29°18'

latitudes and 77°07' and 78°14' East longitudes. It is

roughly rectangular in shape and is bounded in the

north by district Muzaffarnagar, in the south by

Bulandshahr, in the south west by the Union territory

of and in the east by Bijnore and Moradabad

districts. River Yamuna on the west seperates it from

Rohtak and Karnal districts of Haryana.

Meerut and Ghaziabad districts have a monotonous

level plain composed of alluvium. The area is divided

into four physical regions, i.e. the Yamuna Hindon

Doab, the central Depression, Eastern Uplands and the

Ganga khadar. The region has a well developed drainage

system. The rivers Ganga, Yamuna, Hindon and Kali nadi make the main system of drainage.

The study area has a sub tropical monsoon type of

climate. Indian Meterological Department has divided the whole year into four seasons, i.e. cold weather season, hot weather season, the season of general rains and the season of retreating monsoons. The study area lies in the broad belt of alluvial soils. The alluvial soil classified on geological basis into two 3 catagories, old alluvium and new alluvium. The new alluvium or khadar is sandy in texture and light in colour while the older alluvium or bhangar is more clayey and darker in colour.

Meerut and Ghaziabad districts are the most developed and prosperous areas of . They offer optimum conditions for all types of manufacturing activities and are located in an agriculturally productive area which makes the most active development corriodors to Delhi. The study region occupies fertile north-western portion of Upper-Ganga plain which is well endowed with favourable conditions for industrial development. The growing population of the area is directly or indirectly engaged besides agriculture, in manufacturing activities. Industries have helped to solve the unemployment problem created by rapid growth of population and have helped in raising the living standards of the people. This development, however, is associated with some negative environmental impacts.

The rapid urbanisation and increasing concentration of industries has led to unparalled deterioration of the quality of life. Air, water and soil have undergone qualitative change not only in metropolitan areas but :4

also in the rural areas. Pollution, as a negative and

harmful element in environment has become a serious

problem facing the area today.

In order to analyse the impacts of

industrialisation on environmental quality, the whole

thesis is presented in four parts. Part I deals with

physical framework and resource base. It consists of

four chapters. The first chapter deals with relief and

drainage of the study region. Chapter second highlights

climate and soils of the study area. Chapter third

gives an account of existing agricultural resources by

considering general land use pattern, irrigation and

crop land-use. Chapter fourth deals with human

resources in the light of density, growth and distribution of population, level of literacy and urbanisation pattern.

Part II of the thesis related to industrial development and consists of two chapters. Chapter fifth highlights the role of various geographical factors in promoting industries and gives historical background of industrial development. Meerut and Ghaziabad have a large concentration of large, medium and small scale 5 industries but on account of the demand for food grains pressure on land has increased. About 80 per cent of the total area is devoted to cultivation. Due to the massive expansion and intensive utilization of irrigation facilities, Meerut and Ghaziabad have made rapid strides in agriculture. During the decade 1961-71 the area experienced important structural changes in its agricultural economy. About 90 per cent of the total area is irrigated by canals or tubewells. The intensity of irrigation in the study region is much higher than the average intensity of Uttar Pradesh.

Irrigation from tubewells has increased by 40 per cent in from 1960-61 to 1990-91 while

Ghaziabad recorded an increase of 19.55 per cent during this period.

The economy is basically agrarian of the study region. Indirectly it reflects on the industrial development of the region. Industry provides many key inputs which facilitate agricultural development.

Agriculture alone can not solve the problem of the masses. Industrial production, therefore, needs co be stepped up for improving standards of living of the people. The study region offers favourable conditions 6

for industrial development. Availability of extensive

tracts of land along with major highways and a network

of roads passing through the area is a big boost in

promoting industrial development. The situation of

Ghaziabad in close proximity to Delhi has been greatest

stimulant for rapid growth of industries in the region.

Meerut has a large concentration of industries

like sugar mills, distilleries, chemical works, metal

products, agricultural implements, sports goods,

handloom and musical instruments during the last three

decades. Ghaziabad is the biggest industrial area in

the state and the most prominent industrial centres of

the districts are , , Hapur, Mohannagar,

Pilkhuwa, Dadri and Loni. These centres have major

industries like Modi Steel Industry, Modi Spinning mill, Jain Tubes, Amrit Vanaspati, Mohan Meakins, Modi

sugar, Simbhaoli sugar, engineering units and several

chemical and electrical manufacturing units.

The types and distribution of industries in the

study region is discussed in chapter six. It has been observed that highest concentration of large and medium units is mainly seen in the blocks of Razapur, Meerut, -7

Bisrakh, Dadri and Loni. These are developed blocks

from the point of view of industrial establishments.

The blocks of Garhmukteshwar, Dhaulana, Moradnagar in

Ghaziabad district and Jani, Rohta, Rajpura,

Kharkhauda, Parrichatgarh, Machhra, Chhaprauli, Khekra and Pilana in Meerut district do not have any large or medium scale industrial establishments.

It has been observed that small scale industries play an important role in achieving balenced economic growth. There is a large concentration of small scale units in Razapur, Bhojpur, Hapur, Loni, Dadri,

Moradnagar and Simbhaoli blocks of Ghaziabad districts.

A continuous positive growth rate in registered units, employment and production shows that in Meerut district, the number of small scale units has been increasing from 1970 to 1990. In Meerut district,

Baraut block recorded linear growth of (2466.66) per cent in terms of registered units during this period.

Medium positive growth is recorded in (980.0 per cent), (3050.00 per cent), Machhra (1200.00 per cent) and Meerut (603.39 per cent). Parrichatgarh and Baghpat blocks recorded low growth in terms of number of units during 1970-1990. Positive growth in 8 terms of employment in small scale registered units is recorded highest in (1453.33 per cent) while

Meerut (131.47 per cent) and Binoli (70.58 per cent) blocks registered medium positive growth during 1970-

1990. The blocks of Parrichatgarh, Mawana, Baghpat and

Machhra recorded low growth rate in terms of employment in small scale units of the Meerut district. Production grwoth rate in small scale units recorded highest in

Baraut (7692.20 per cent) while low growth recorded in

Kharkhauda (23.16 per cent) during 1970-1990.

In the study region, polluting industries nave been identified by the Central Board for Prevention and

Control of Pollution. These industries are chemical, sugar, distillery, tannaries, pulp and paper, textiles, dye stuff, fertilizer and pharmaceuticals units. The main industries discharging their waste into Hindon and

Kali nadi are sugar factories, metallurgical and processing work.

Crucial analytical study of industrial development and its impact on environment is discussed in Part III.

This part consists of three chapters from chapter .jeven to nine. Chapter seven gives a general assesmsut of 9 nature and spread of environmental pollution by emphasising air, water, noise and land degradation.

Chapter eight and nine discuss the impact of

industrilisation on environment is studied by considering various aspects of pollution through Factor

Analysis in respect of habitat quality, land degradation, quality of life, air pollution, water pollution and noise pollution. The first factor analysis delas with the city areas of both Meerut and

Ghaziabad districts while the second factor analysis relates to several aspects of environmental pollution in selected towns and other urban areas of the study region. The environmental pollution of the region ultimately points to several related diseases that are degrading health of the people in the study area.

The results of the first factor analysis concerning habitat quality in Meerut and Ghaziabad city areas are given in chapter eight shows that flooding of drains, foul smell and garbage spread are the main cause of degrading habitat conditions. Domestic refuse are the main causative factor of land degradation. The other items that also play an effective role in degrading land quality are garbage collection once a to week and people of these localities dipose their garbage on the streets in both city areas of the study

region. In few areas, garbage is collected through municipal collection sites but their process of

collection is quiet irregular. Shortage of water

supply, lack of health facilities low income group people, congestion/lack of open space are the main positively related items that are degrading quality of

life. Vehicular traffic and waste disposal are the main

items of spreading air pollution. Water logging, waste water from houses, dairy animals and industries are major contributing items in increasing water pallution.

The main sources of noise in the city areas are vehicular traffic and loudspeakers.

Environmental pollution ultimately leads to various pollution related diseases that are degrading the quality of health of people living in city areas of

Meerut and Ghaziabad districts. Air pollution results in various diseases of which asthma, bronchitis, nausea, eye-irritation and skin diseases are positively related in the localities of the study region. Water pollution leads to many diseases that affect the health 11 of people. Diarrhoea, jaundice, throat infection, cholera, dysentry and other diseases are the main water borne diseases in the study region.

In the ninth chapter, the results of the second factor analysis performed for the fifteen sample stations of the study region in the form of rotated factor matrix for each of the sample station highlight three factors concerning habitat quality, land degradation, quality of life, air pollution, water pollution and noise pollution. Pollution related diseases were also indentified in each sample station.

The results of the study indicate that flooding of drains and foul smell are the main cause of unhygienic conditions in all the sample points except in of Meerut district. Over-crowding plays a leading role in Abdullahpur, Mawana, Daurala, Baraut and Baghpat.

Fumes/smoke recorded positive association with degradation of habitat quality in all the sampling station excepting Sardhana and Kharkhauda. Similarly flooding of drains is a common phenomenon in all the sampling points except in of Ghaziabid district. Over-crowding disturbs habitat quality in

Babugarh, Hapur, Dadri, Modinagar and Loni areas. Foul 12

smell creates problem for the residents of Babugarh,

Hapur, Modinagar, Loni and Noida while the remaining •

stations Dadri, Moradnagar and Garhmukteshwar are not

affected in this regard. Garbage found in heaps in

Babugarh, Dadri, Noida and Moradnagar and' garbage

spread on land in Hapur, Modinagar, Loni, Noida and

Garhmukteshwar. Fumes/smoke also affect living

conditions in different locations.

Domestic refuse causes land degradation in all the

sampling areas of the study region. The other items of

land degradation are garbage, industrial refuse and

brick bhatts. Shortage of electricity, lack of health

facilities and shortage of water supply are responsible

for degradation of quality of life in all the sampling

stations of the study region except Daurala, Babugarh,

Dadri, Mawana, Hapur, Modinagar, Loni and Noida,

vehicular traffic helps in spreading air pollution.

Waste-water from houses leads to water pollution in all

the sampling areas except Hapur and Noida.

Water logging creates problem in areas of

Abdullahpur, Mawana, Daurala, Baraut, Baghpat,

Kharkhauda, Babugarh, Hapur, Noida, Moradnagar, 13

Garhmukteshwar and Loni. It is also seen that vehicular

traffic and loudspeakers used at various functions

increase noise level in all the sampling areas of the

study region except in Abdullahpur.

Air pollution in the study region leads to several

related diseases that affect people. The most common diseases that affect the health of the people in almost

all the sample areas of Meerut district are eye-

irritation, headache, nausea, bronchitis asthma except

in Mawana and Kharkhauda where bronchitis and asthma is not positively correlated. Similarly, in Ghaziabad district eye-irritation, headache and nausea are the main diseases that are deteriorating the health of the people except in Moradnagar and Noida.

Water pollution of the study area gives rise to many diseases. Diarrhoea, jaundice and dysentry are the main water borne diseases in all the selected areas of

Meerut district except in Abdullahpur where dysentry is not present. In Ghaziabad dysentry and diarrhoea are revealed as the main water related diseases in all the sampling areas except Dadri. Typhoid is the second water related disease of all the sampling areas but in

Hapur and Moradnagar it is not positively correlated. 14

Throat infection, cholera, kidney stones and some other diseases also affect health of the people residing in the study region.

Part IV of the thesis is devoted conclusion and suggestions. Here measures have been suggested to overcome the problem of environmental degradation and for minimising environmental pollution for balanced industrial development in the study region. ENVIRONMENTAL CONSEQUENCES OF INDUSTRIAL DEVELOPMENT -A CASE STUDY OF MEERUT AND GHAZIABAD DISTRICTS

THESIS SUBMITTED TO ALIGARH MUSLIM UNIVERSITY FOR THE AWARD OF THE DEGREE OF MottOV Of P[)!lQgOp!)P IN GEOGRAPHY

UNDER THE SUPERVISION OF PROF. M. FAROOQ SIDDIQI

DEPARTMENT OF GEOGRAPHY ALIGARH MUSLIM UNIVERSITY ALIGARH (INDIA) 1995 DEDICATED TO MY PARENTS FOR THEIR LOVE, SUPPORT AKD ENCOURAGEMENT

\ T4926

'

>,

CH3CTEE-2002•m " phrno.(571)400883 Kim cfareeq Zjiddiqi Phone. 400520 to 22 Ext. 210 DEPARTMENT OF GEOGRAPHY PROFESSOR AUGARH MUSLIM UNIVERSITY ALIGARH-202002, INDIA

This is to certify that the thesis entitled, "Environmental Consequences of Industrial Development: A case study of Meerut and Ghaziabad Districts" has been completed by Miss Nigar Anjum under my supervision. Her thesis is an original piece of research and I am sure it will prove to be a great

0 contribution to the field of environmental quality.

(M. Farooq SiddiqjL)

Residence ; SF Manzil. Firdaus Colony, 4^474 podbpur, Aligarb-202002 Phono: (571)402346 CONTENTS PAGE NO. ACKNOWLEDGEMENT i-li LIST OF FIGURES iii-iv LIST OF TABLES v-xii INTRODUCTION xiiVxxv PART I PHYSICAL FRAMEWORK AND RESOURCE BASE

CHAPTERS I RELIEF AND DRAINAGE 1-12

1.0 Relief 1 1.1 Physical divisions 2 1.1.1 The Yamuna Hindon Doab 2 i.i.2 The central depression 3 1.1.3 The eastern uplands 3 1.1.4 The Ganga Khadar 4 1.2 Drainage 5 1.2.1 Ganga 5 1.2.2 Yamuna 7 1.2.3 Kalinadi 8 1.2.4 Hindon 9 1.2.5 Krishni 1.) 1.2.6 Banganga 10 1.2.7 Minor streams 10

II CLIMATE AND SOILS 13-30

2.0 Climate 13 2.0.1 Cold weather season 14 2.0.2 Hot weather season 17 2.0.3 The season of general rains 18 2.1 Soils 24 2.1.1 Khadar Soils 25 2.1.2 Bhangar soils 27 2.1.2.. 1 Loamy soils 27 2.1.2.. 2 Clayey soils 2 8 2.1.2., 3 Sandy Loam 29 2.1.2., 4 Alkaline soils 30

III AGRICULTURAL RESOURCES 31-51

3.0 General land use 31 3.1 Irrigation 33 Intensity of irrigation 37 Crop land use 41 Intensity of cropping 43 Fertilizer consumption 45

HUMAN RESOURCES 52-76

Population 52 Growth of population 54 Density of population 55 Literacy 58 Distribution of population 62 Urbanisation 62 Town classification 67 Standard Urban Areas 67 1 MEERUT . 67 2 GHAZIABAD 71 3 MODINAGAR 73 4 HAPUR 74 Persons engaged in non-agricultural 76 activities

PART II INDUSTRIAL BASE

INDUSTRIAL DEVELOPMENT 77-92

Historical background 77 Geographical basis 87 Climate 88 Raw materials 89 Transportation 90 Population 90

INDUSTRIES: TYPES AND DISTRIBUTION 93-132

Large-scale industries 93 Distribution of large scale industries 102 Small-scale industries 105 Small-scale industries in Meerut 106 district Small-scale industries in 107 Ghaziabad district Blockwise registered units of small 110 scale industries in Meerut district 6.2.4 Blockwise employment of small scale 114 industries in Meerut district 6.2.5 Blockwise production of small scale 118 industries in Meerut district 6.3 Polluting industries 121

PART III POLLUTION: NATURE AND SPREAD

VII ENVIRONMENTAL POLLUTION: GENERAL 133-175 ASSESMENT

7.0 Environmental Pollution 133 7.0.1 Air pollution 135 7.0.2 Water pollution 140 7.0.3 Land Degradation 147 7.0.4 Noise pollution 155 7.1 Review of studies conducted in Meerut 157 and Ghaziabad districts. 7.2 Industrial pollution in Meerut and 167 Ghaziabad districts. 7.2.1 Water pollution 168 7.2.2 Air pollution 171 7.2.3 Noise pollution 172 7.2.4 Garbage pollution 173 7.2.5 Social pollution 175

VIII CASE STUDIES: METROPOLITAN CITIES 176-215

8.0 Technique of Analysis 176 8.1 Case studies in Meerut and Ghaziabad 178 cities 8.1.1 Habitat quality 178 8.1.2 Land degradation 184 8.1.3 ^ Quality of life 189 8.1.4 Air pollution 194 8.1.5 Water pollution 198 8.1.6 Noise pollution 203 8.1.7 Water borne diseases 207 8.1.8 Air borne diseases 211

IX CASE STUDIES: SMALL TOWNS AND URBAN 216-361 AREAS

9.0 ABDULLAHPUR 216 9.1 MAWANA 227 9.2 DAURALA 237 9.3 BARAUT 246 9.4 SARDHANA 255 9.5 BAGHPAT 265 9.6 KHARKHAUDA 274 9.7 BABUGARH 284 9.8 HAPUR 293 9.9 DADRI 303 9.10 MODINAGAR 312 9.11 NOIDA 323 9.12 MORADNAGAR 332 9.13 LONI 342 9.14 GARHMUKTESHWAR 351

PART IV CONCLUSION AND SUGGESTION

CONCLUSION 362-392

10 .0 Relief and drainage 363 10 .1 Climate and soils 363 10.. 2 Agricultural resources 364 10 .3 Human resources 366 10,. 4 Industrial development 366 10 .4 .1 Large and small scale industries 367 10.. 4 .2 Small scale industries 368 10..4 .. 3 Polluting industries 369 10,. 5 Factor Analysis 370 10..5 ,. 1 Factor Analysis in Metropolitan Areas 370 of Meerut and Ghaziabad districts 10..5 ,. 2 Factor Analysis in selected towns and 372 Urban Areas of the study region 10,.5 ,.2 .. 1 Habitat quality 372 10..5 ,.2 ,. 2 Land degradation 374 10,.5 ..2 .. 3^-Qualit3 y of life 377 10..5 ..2 ,. 4 Air pollution 380 10.,5 .,2 ., 5 Water pollution 383 10..5 ..2 ., 6 Noise pollution 385 10..5 ..2 ., 7 Air borne diseases 387 10.,5 .,2 . 8 Water borne diseases 389

XI SUGGESTIONS 392--405 SELECTED BIBLIOGRAPHY 406--410 APPENDIX - A - questionnaire 411- 414 ACKNOWLEDGEMENT

I wish to express my profound sense of gratitude and indebtedness to Prof. M. Farooq Siddiqi, Department of Geography, Aligarh Muslim University, Aligarh for his valuable guidance, constant help and encouragement in pursuing the research and presenting it in the form of a thesis.

I am also thankful to Prof. (Mrs.) Abha Lakshmi

Singh, Chairperson of Department of Geography and Prof.

K.Z. Amani, ex-Chairman for extending all the necessary library facilities and for generating conducive research atmosphere in the department.

Prof. Mehdi Raza and Prof. Abdul Aziz were always ready to help me in my endeaviour and were a constant source of encouragement. I am greatly indebted to them for their help.

My sincere thanks are also due to Dr. Abdul Munir and Dr. Farasat Ali Siddiqi, Readers in Geography at

A.M.U. for their constant help and suggestions during the course of writing this thesis.

Thanks are also due to Mr. Najmuddin of

Departmental Seminar Library for providing all the necessary research material. In last, but not the least my humble feelings of

gratitude are always towards my parents and sisters

whose encouragement and affection has always been a

source of inspiration for me during my entire academic pursuits.

(NI5AR ANJXJM) LIST OF FIGURES

Figure no. Page no

1 Meerut and Ghaziabad districts- XVII Administrative Divisions-1991

2 Meerut and Ghaziabad districts-Drainage 6

3 Meerut and Ghaziabad districts- 21 Temperature and relative Humidity

4 Meerut and Ghaziabad districts- 36 Irrigation 1990-91

5 Meerut and Ghaziabad districts- 40 Irrigation Intensity 1990-91

6 Meerut and Ghaziabad districts-cropping 47 intensity 1990-91

7 Meerut and ' Ghaziabad districts- 49 Fertilizer consumption 1990-91

8 Meerut and Ghaziabad districts-Density 57 of Population 1981

9 Meerut and Ghaziabad districts-Literacy 60 rate 1981

10 Meerut and Ghaziabad districts- 64 Distribution of Population-1981

11 Meerut and Ghaziabad districts-Means of 91 Transport

12 Meerut district-small scale registered 108 units, employment and production-1970- 1990

13 Meerut district-Small scale registered 113 units 1970-1990

14 Meerut district-Employment in small 117 scale industries 1970-1990 15 Meerut district-Production of small 119 scale industries 1970-1990

16 Meerut and Ghaziabad districts-polluting 124 industries

17 Sample stations of Meerut city 177

18 Sample stations of Ghaziabad city 180

19 Meerut and Ghaziabad districts-Sample 217 station V

LIST OF TABLES

Table No. Page No.

I Temperature and relative humidity 15 in Meerut district.

II Temperature and relative humidity 19 in Ghaziabad district

III General land-use of Meerut and 32 Ghaziabad districts 1966-67-1990- 91.

IV Intensity of irrigation in Meerut 37 and Ghaziabad districts.

V Irrigation by different sources in 38 Meerut district.

VI Irrigation by different sources in 39 Ghaziabad district

VII Blockwise irrigation intensity in 42 Meerut and Ghaziabad districits 1990-91.

VIII Crop land-use in Meerut and 43 Ghaziabad district

IX Intensity of cropping in Meerut 44 and Ghaziabad districts 1960-61- 1990-91.

X Intensity of cropping in Meerut 46 and Ghaziabad districts, 1990-91.

XI Use of chemical fertilizers in 50 Meerut and Ghaziabad districts.

XII Fertilizer consumption in Meerut 51 and Ghaziabad districts.

XIII Economic classification of 54 population 1990-91. XIV Growth of population 1951-1991. 55

XV Density of population 1981. 56

XVI Literacy in Meerut and Ghaziabad 61 districts

XVII Distribution of population in 63 Meerut and Ghaziabad districts 1981.

XVIII Percentage of urban population, 67 growth rate, sex ratio and Density 1981-1991.

XIX Population of urban agglomarates, 68 cities and towns of Meerut districts, 1991.

XX Population of urban agglomarates, 69 cities and towns of Ghaziabad district, 1991.

XXI Standard urban Areas and growth of 70 population of core towns, 1991.

XXII Persons engaged in non- 75 agricultural activities.

XXIII Large and medium scale industries 104 of Meerut district.

XXIV Large and medium scale industries 104 of Ghaziabad district.

XXV Small-scale industries of 109 Ghaziabad district 1985.

XXVI Small scale industries of 110 Ghaziabad district (1985-1990) .

XXVII Small-scale registered units in 111 Meerut distract (1970-1990) . XXVIII Employment in small-scale 115 industries in Meerut district (1970-1990) .

XXIX Production of small-scale 120 registered units in Meerut district (1970-1990) .

XXX Polluting industries of Meerut 125-126 district.

XXXI Polluting industries of Ghaziabad 128-130 district.

XXXII Types and sources of environmental 135 pollution.

XXXIII Major air pollutants: Sources and 138 effects.

XXXIV Water pollutants in major 143-144 industries.

XXXV Maximum Decibel count in Indian 157 cities.

XXXVI Estimation of pesticides present 162 in Kalinadi at Meerut district.

XXXVII Toxic metals in Kalinadi at 163 Modinagar in district Ghaziabad.

XXXVIII Pesticides detection in different 164 food stuffs in Meerut.

XXXIX Air pollution in Meerut city 166

(1991-92) .

XL Habitat quality in Meerut city. 179

XLI Habitat quality in Ghaziabad city. 183

XLII Land degradation in Meerut city. 185

XLIII Land degradation in Ghaziabad 187 city. XLIV Quality of life in Meerut city. 190

XLV Quality of life in Ghaziabad city. 191

XLVI Air pollution in Meerut city. 195

XLVII Air pollution in Ghaziabad city. 196

XLVIII Water pollution in Meerut city. 199

XLIX Water pollution in Ghaziabad city. 201

L Noise pollution in Meerut city. 204

LI Noise pollution in Ghaziabad city. 205

LII Water borne diseases in Meerut 208 city.

LIII Water borne diseases in Ghaziabad 209 city.

LIV Air-borne diseases in Meerut city. 212

LV Air-borne diseases in Ghaziabad 213 city.

LVI Habitat quality, Land degradation 219 and quality of life in Abdullahpur

LVII Air pollution, Water pollution and 222 Noise pollution in Abdullahpur.

LVIII Pollution related diseases in 225 Abdullahpur.

LIX Habitat-quality, Land-degradation 229 and Quality of life in Mawana.

LX Air pollution, Water-pollution and 232 Noise pollution in Mawana.

LXI Pollution related diseases in 234 Mawana. LXII Habitat-quality, Land degradation 239 and Quality of life in Daurala.

LXIII Air pollution, Water pollution and 241 noise pollution in Daurala.

LXIV Pollution related diseases in 244 Daurala.

LXV Habitat-quality, Land degradation 248 and Quality of life in Baraut.

LXVI Air pollution, water pollution and 251 noise pollution in Baraut.

LXVII Pollution related diseases in 254 Baraut.

LXVIII Habitat-quality, land degradation 257 and quality of life in Sardhana.

LXIX Air pollution, water pollution and 260 noise pollution in Sardhana.

LXX Pollution related diseases in 263 Sardhana.

LXXI Habitat-quality, land degradation 267 and quality of life in Baghpat.

LXXII Air pollution, water pollution and 270 noise pollution in Baghpat

LXXIII Pollution related diseases in 272 Baghpat.

LXXIV Habitat quality, land degradation 276 and quality of life in Kharkhauda.

LXXV Air pollution, water pollution and 279 noise pollution in Kharkhauda.

LXXVI Pollution related diseases in 282 Kharkhauda. XCII Habitat quality, land degradation 334 and quality of life in Moradnagar.

XCIII Air pollution, water pollution and 337 noise pollution in Moradnagar.

XCIV Pollution related diseases in 340 Moradnagar.

XCV Habitat quality, land degradation 344 and quality of life in Loni.

XCVI Air pollution, water pollution and 347 noise pollution in Loni.

XCVII Pollution related diseases in 349 Loni.

XCVIII Habitat quality, land degradation 353 and quality of life in Garhmukteshwar.

XCIX Air pollution, water pollution and 356 noise pollution in Garhmukteshwar.

C Pollution related diseases in 359 Garhmukteshwar.

CI Average factor loadings for items 373 affecting habitat-quality in Meerut and Ghaziabad districts.

CII Average factor loadings for items 375 affecting land degradation in Meerut and Ghaziabad districts.

CIII Average factor loadings for items 37 8 affecting quality of life in Meerut and Ghaziabad districts.

CIV Average factor loadings for items 381 affecting Air pollution in Meerut and Ghaziabad districts. XII

CV Average factor loadings for items 384 affecting water pollution in Meerut and Ghaziabad districts.

CVi Average factor loadings for items 386 affecting noise pollution in Meerut and Ghaziabad districts.

CVII Average factor loadings of Air- 388 borne diseases in Meerut and Ghaziabad districts.

CVIII Average factor loadings of Water- 390 borne diseases in Meerut and Ghaziabad districts. INTRODUCTION

India, being a developing country is striving at its best for rapid development of its industry, agriculture, science and technology, means of transport and communication but associated with developmental activity, the problem of environmental pollution is inevitably present in every human survival enterprise and ultimately poses a threat to human survival. The entire law relating to prevention and control of environmental pollution is a result of our anxiety and preference to human survival over development, progress and prosperity. It is true that any developing country can prosper only with industrialisation. The industries have helped to solve unemployment problem created by rapid growth in population but they side by side lead to environmental pollution to such an extent that the life of people is affected in various ways. Everyone thus agrees about the importance of development for raising the living standards and affording a better quality of life to the people but it is certain that major development is associated with some negative environmental impacts.

Since independence in 1947, India has made tremendous progress on all economic fronts. It is today

among the ten industrialised nations of the world. Self

reliance has been achieved in core sectors such as iron

and steel, crude refining, engineering goods, food and

food processing, building materials, consumer goods and

other essential commodities. Such major industrial

transformation is bound to disturb ecological balance.

It has generated huge quantities of solid, liquid and

gaseous pollutants. The over all impact of the

existence of industries on urban environment is seen in

the increase in smoke, noise, heat, gas, fumes etc.

which not only affect human health but also damage

properties. Industries also cause land pollution as a

result of dumping of solid wastes in open areas which

get leached into the soil and pollute the soil as well

as the ground water.

It is obvious that man is responsible for polluting

the geo-environment in improper shape. Development

however, is necessary to remove poverty and feeding the

growing population or maintaining the standard of

living. India needs fast development for its increasing population in the field of agriculture, power generation, industry, transport but the development should be sustainable. Today, protecting and maintaining the balanced ecosystem has become a major task. There is greater awareness of environmental issues today but unfortunately attention is largely drawn to global issues rather than local issues.

Study Area

In view of the importance of environmental consequences as a result of industrial development, the author in the present work has tried to assess the role of various factors which contribute in deteriorating environmental quality of Meerut and Ghaziabad districts. Meerut and Ghaziabad districts have been selected as the study area because this region offers optimum conditions for location of all types of manufacturing activities and is located in an agriculturally productive area. It is one of the most active development corriodors around Delhi and has close linkages with the National Capital Region. The study area lies between 28° 29' North and 29° 18' North latitudes and 77° 07' East and 78° 14' East longitudes.

The area is roughly rectangular in shape and is bounded in the north by district Muzaffarnagar in the south by Bulandshahr in the southwest by the union territory of

Delhi and in the east by Bijnore and Moradabad districts. River Yamuna on the west separates the area from the Rohtak and Karnal districts of Haryana

(Fig.l).

Meerut and Ghaziabad districts cover an area of

6505 sq. kilometers. The total population in 1991 was

6185,892 persons according to the census of India.

Administratively, the study area is divided into 8 tehsils and 28 blocks and it had 36 towns and 1624 villages in 1991. The region occupies fertile northwestern portion of upper Ganga plain which is well endowed with favourable conditions for industrial development.

The study region is a monotonous level plain composed of old alluvium, bhangar and new alluviam, khadar and has a well developed drainage system. The area has a subtropical monsoon type of climate.

Availability of large tracts of level lands along the major highways and many regional level roads passing through the study region are favourable for the location and development of various types of T T •a •S5 I

Ui u *. < >• ,_ S £ •- a S 5 a a < < < ? o < o 2 = o < d d = Z iu O O 0 ? I < < • - - x x 1 O c/> X O -J — UJ -J t- 0 o <- at o O • •£ XVIII industries. The location of Ghaziabad and Meerut in close proximity to Delhi together with large in migration as a result of partition of the country in

1947 have acted as great stimulant to the rapid growth of industries in this region.

Objectives of the Study

The main objectives of the study are :

1. To asses the physical base of the region which

provide basic framework for the development of the

study region.

2. To study and analyse the existing resources of the

region.

3. To take into account the industrial background of

the study region.

4. To asses and analyse the growth and distribution

of large, medium and small scale industries and

major polluting industries of the study region.

5. To asses and analyse the factors that are

contributing their role in spreading pollution in

the city areas of Meerut and Ghaziabad districts.

6. To examine the nature and spread of environmental

pollution including air, water, noise and land

degradation. 7. To examine the consequences of environmental pollution in different selected towns and urban centres of the study region including habitat quality, land degradation, quality of life, air pollution, water pollution and noise pollution. 8. To suggest suitable measures for improving environmental conditions and for balanced industrial development in Meerut and Ghaziabad districts.

Data base

The study is mainly based on primary data gathered through questionnaire survey. Besides, Secondary data has also been collected from relevant documents, guidelines, reports and unpublished records of the Government of India and the state Government of Uttar Pradesh.1

1. Secondary data was obtained from : District census Handbook of Uttar Pradesh, (1971,1981, 1991) published by Directorate of census operations, Lucknow, uttar Pradesh. District Statistical Bulletin (1970,1980,1990) published by Economics and Statistics, Lucknow, Uttar Pradesh. Directory of Small-Scale Industries (1970, 1980, 1990) published by District Industries Centre, Meerut and Ghaziabad districts. The study concerns two districts, Meerut and

Ghaziabad, for which the published data at district level was available only for Meerut district from 1965 to 1990. But Ghaziabad district was formed in 1976 and therefore, the data for this district has been taken from 1980 to 1990. On the basis of the detailed questionnaire survey (Appendix 1) people of city areas of Meerut and Ghaziabad districts were interviewed to asses the impact of industrial development in the region. The questionnaire was prepared to gather information about habitat quality, land degradation, quality of life, air pollution, water pollution and noise pollution. The environmental pollution of the region results in various related diseases that are affecting the health of the people and data was gathered for this aspect also.

For detailed study, five localities of each metropolitan area were selected as representative conditions prevalent in congested area, noisiest area, residential area, industrial area and planned localities of the region. The sample design adopted was thus purposeful. Another detailed study was conducted after selecting fifteen urban areas and small towns of XXI

the study region. These fifteen representative areas were randomly selected from all over the region. Care was however, taken to select areas which were well

distributed in the region and thus represent the over

all conditions of the area. The topographical maps of

the scale of 1 : 20,000 have formed the basis for

studying the morphology of sample stations of the study

region.

Methodology

The following statistical methods have been used in the present study :

1. The original data of number of establishments, production and employment figures were plotted by using trend line graph, which have equation of the form :

Y = mx + c where x and Y are variables and m and c are constants which determine the gradient of the line and where it cuts the y axis respectively.

E (xy) Ey m= c= =Y

E(x)2 n

Y = mx + c or Y = a + bx

2 . The values of the city area survey for Meerut and

Ghaziabad districts have been computed for 10 XXII

localities of both the districts. The Factor Analysis

for 10 x 6 data matrix condensed 37 variables to form 6

compound factors for total city areas of Meerut and

Ghaziabad districts.

On the other side, the values of the ,„37 variables

have been computed for 15 selected areas of both Meerut

and Ghaziabad districts. The factor Analysis of 15 x 6

data matrix also condensed 37 variables to form 6

compound groups for each selected area of the two

districts.

The methodology of Factorial ecology developed in

early 1960's employs a large variety of mathematically

rigorous methods of Factor Analysis to reduce large

number of socio-economic and environmental indicators

into a few underlying dimensions. The factor analysis

attempts to assess the values of regression

coefficients where the original variables are regressed

on the factors. The coefficients of regression are

termed as factor loading's. Factor loadings give a set

of new factor loadings it further processed by

rotations.

Computation of these analysis was carried on

VAX/VMS (VAXII) computer system. Factor analysis was XXIII

completed through following steps :

1. A principal component solution and the varimax

rotation of the factor matrix is performed.

2. The varimax rotation is used to simplify columns

rather than rows of the factor matrix. In order to

keep the number of independent dimensions

(variables) as small as possible. Only those eign

values greator than or equal to 1.0 are retained

in the analysis.

The subroutines used in the calculation of factor analysis are : CORRE, EIGEN, TRACE, LOAD and VARMX. The items calculated through these subroutines are : Mean,

Standard Deviation, Inter Correlation of variables, eigen values, cumulative percentage of eigen values,

Eigen vectors, Factor matrix, variance of the factor matrix for each interaction cycle and rotated factor matrix.

Thesis Plan

The present work is divided into four parts spread over eleven chapters. Part I relates to the physical framework and resource base of the area. It consists of four chapters of which the first two relate to XXIV highlight the relief, drainage, climate and soils of the area. The third chapter gives an account of existing agricultural resources of the region by considering general land use pattern, irrigation and cropland-use. Chapter fourth discusses human resources in the light of density, growth and distribution of population, level of literacy and urbanisation pattern.

Part II of the thesis deals with industrial development and consists of two chapters. Chapter Vth highlights the role of various geographical factors in promoting industries and gives historical background of industrial development. Chapter sixth considers large, medium and small scale industries and in the light of linear growth rate determines the levels of industrial development in the study region. This chapter also examines the role of polluting industries in deteriorating environmental quality of Meerut and

Ghaziabad districts.

Crucial analytical study of industrial development and its impact on environment is discussed in Part III.

Chapter seven to nine gives a general assessment of nature and spread of environmental pollution by emphasizing air, water, noise and land degradation. A review of literature with environmental set up and industrial character of the region is also examined.

Various aspects of environmental pollution in the study region are analysed in chapter eight and nine, chapter eight relates to various aspects of Meerut and

Ghaziabad and cities to determine habitat quality, land degradation, quality of life, air pollution, water pollution and noise pollution in the city area through

Factor Analysis. In the ninth chapter various aspects of environmental pollution are analysed for various places selected amongst small towns and from urban areas of both Meerut and Ghaziabad districts.

Finally, Part IV of the thesis is devoted to conclusion of the study in chapter ten and suggestions in chapter eleven regarding measures that can be undertaken to overcome the problem of environmental degradation and for balanced industrial development in the study region. PARTI

PHYSICAL FRAME WORK AND RESOURCE BASE 1

CHAPTER I

RELIEF AND DRAINAGE

1.0 The topography of the region shows almost a level

alluvial plain with a slight slope from north to south

or southeast. The monotony of level surface with

imperceptible slope is broken by some ravines developed

near the river valleys and a few scattered small sandy

ridges found in the upland tract.

The main features that affect the plain are the

river Yamuna, Ganga and Hindon whose valleys are of varying width and are on a lower level than the main upland tract. The flood plain of these rivers are small but the transition from the river valleys to the upland

is marked by the ravines and erosion or by sloping sandy undulations. Along the Ganga and away from it the soil has deteriorated for a considerable distance and much of the area is occupied by long stretches of sandy soil. The soil along river Yamuna is not so damaged.

The Khadar of the Hindon is comparatively narrow and the deterioration is generally confined to the immediate neighbourhood of the river and it is only when the Hindon and the Yamuna come closer in the south western corner of the district on a narrow stretch of 2 inferior soil is met with. The only part that is liable to be flooded are the Ganga khadar in the Mawana and

Garhmukteshwar tehsil, some areas in the low lying tract of Loni and those in the south of Baghpat near the river Yamuna.

1.1 Broadly speaking the area on the basis of appearence and formation can be divided into four micro

- physical regions :

1.1.1 The Yamuna Hindon Doab

The tract lies between the Yamuna on the west and the Hindon on the east includes the whole of tehsil

Baghpat, a portion of tehsil Sardhana and the district of Ghaziabad from a width of over 40 kilometers in the north and it narrows down to a point in the south where these two rivers tend to converge. The tract in general is the most fertile portion of the district consisting of rich and almost uniformly loamy soil and is flanked by belts of poor soil and broken relief associated with the two rivers. The tract is bounded by the Hindon on the east and by a high ridge (which seperates the uplands from the Yamuna khadar) on the west. The terrain is generally broken up by small ravines, a lowlying of Yamuna - Hindon khadar are lies to the 3 south of the ridge. With it numerous shallow depressions it as much wider in the south than in the northern part of the tract. There are a number of sandy mounds along the banks of the Yamuna and Hindon and its tributary, Krishni and Ganga.

1.1.2 The Central depression

This tract lies roughly between the Hindon and the

Kali nadi includes the western part of tehsils Sardhana and Meerut, eastern parts of tehsil Dadri and parts of

Hapur. This is a well drained tract except for a small patch near Dhaulana in tehsil Hapur and contains some of the most fertile land in the district. East of the

Ganga canal the slope of the land as far as the centre of the tract is towards the east but from these onwards there is a rise on the Meerut-Hapur-Bulandshahr road.

Several drains have been constructed in this section but even these artificial aids do not achieve the object of draining the water. The soil here is good but has a tendency to become over saturated and gives rise to the formation of saline deposites which are rare in other parts of the districts except in the khadar tract.

1.1.3 The eastern uplands 4

This tract comprises the area between the central depression and the ravines of the river Ganga and includes the eastern portion of tehsil Hapur and

Mawana, parts of Meerut, Sardhana and whole of

Garhmukteshwar. It is drained by Kali nadi (east) and its tributary stream, one of its important features is the exsistance of a series of sandy strips sometimes occuping in the form of perpendicular broad front which are generally confined to the vicinity of this river and the Ganga, one of these ridges runs diagonally southeast from the point where the Kali nadi enters in district Bulandshahr. These bhur strips owe their origin to an admixture of sand in the stratum and the action of wind. In between these ridges there are fairly extensive stretches of level plain. However, the entire eastern portion is broken by fluvial erosion along the river Ganga. Further south to the east of

Hapur there is also sand and the western flank is eroded and scarred Kali nadi (east) and its tributaries .

1.1.4 The Ganga khadar

The eastern tract is low khadar on flood plain or the river Ganga. This tract is characterised by the 5 existance of several depressions and water courses generally connected with the river. It is bordered on the west by the old high river bank and this particular area is covered with ravines.

DRAINAGE

1.2 The character of the surface drainage shows a close relationship with the gentle slope of the land.

It would perheps be best to study the surface drainage under two heads : the rivers and the lakes. The principal rivers are the Ganga, the Yamuna, the Hindon and the Kali nadi, (Fig. 2). The Ganga and the Yamuna have their sources in the snowy caps of the Himalyas, the Hindon rises in the Shiwalik hills and the other rivers rise from the lake in the plains. The minor streams of the area are seasonal in nature. The principal rivers of the study region from east to west are the Ganga, the Hindon, the Yamuna and the Kali nadi .

1.2.1 The Ganga

The Ganga has a very large basin and it is the most important river of this region. After rising in

Gangotary glacier in the Himalyas, it enters the upper doab plain at Haridwar through a well defined gorge in fj ( the Shiwaliks. Its general direction is from north to south and on the eastern side it seperates this region from the district of Moradab2ad and Bijnor.

The bed of the river is sandy and the underlying stratum is of the nodular lime stone here and there.

The volume and velocity of the river vary at different periods of the year with greatest amount during July and August. Its banks generally suffer from slow erosion and the soil of the khadar village which lies adjacent to it from increasing infertility due to the sandy deposits during the floods in monsoon months.

1.2.2 Yamuna

The river Yamuna enters the district north of village Tanda in Chhaprauli block and flows southwards forming the boundary of the district as far as the point where the district of Meerut, Delhi state and the district of Rohtak (in Punjab) meet. From here it leaves the boundary between the district and Delhi state till it finally goes out of the district adjacent to village Harampur of Loni block of Ghaziabad district. There is considerable variation in the height of its left bank which in tehsil Baghpat is characterised by the existance of steep and abrupt 8 ridges some of which are flat and comprise the sites of largest habitations. The small lowlying areas between the bank and the river are often affected by the floods which benefits the soil by leaving alluvial deposits.

In chhaprauli, Kotna and Baghpat it takes a slight bend to the west for a few kilometers. In times of heavy floods it approches the outskirts of these places which are all situated on the crest of the high bank. Further south, the bank is not high as a result of which some part of the Loni block are often flooded. The bed of the river is so low in places that irrigation is impracticable and its water is only used for the cultivation of melons which grows on its sandy banks and are much prized for their excellence.

1.2.3 KALI NAD I

The river is also known as Nagin, (probably on account its serpentime windings) and also as the Kali nadi (east) to distinguish it from Kali nadi (west) , a tributary of the Hindon. Generally, it traverses undulating sandy slopes which are rarely cut up into ravines. The river carries very little water except during the rains. It joined its course by three smaller streams, two of which are known by the generic name of 9 chhoiya.

1.2.4 Hindon

The river enters the district of Meerut from

Muzaffarnagar at the village of Pitlokhar (in tehsil

Sardhana) and flows south west in a tortuous course till it leaves the district near the village of

Mongrali in tehsil Dadri. The width of the river varies from half kilometers in the hot weather to about 1.75 kilometers in the rains. It is fordable for most of the year except during the rains when it becomes nevigable.

It is used as a sort of link between the Ganga and the

Yamuna, as it receive the superfluous water of the former from the tail end of the Deoband canal near

Budhana (in ) and conveys it into the Yamuna through an artificial channel just below the railway bridge near Ghaziabad.

The Hindon is an active river from the point of view of soil erosion. The khadar land of the river varies in width at different places and extend to 1.75 kilometers on each side of the stream. As the river proceeds southward, the khadar widens out of both sides of its bank. Although it is affected by reh, its water is used for irrigating rabi crops. 10

1.2.5 krishni The Karruni or Krishni, a small stream between the

Yamuna and Hindon enters the district near Tikri

village and after flowing in a well marked bed it joins

the Hindon near village Barnawa. It is an insignificant

stream with no towns on its banks and is little used

for irrigation.

1.2.6 Banganga

Another insignificant stream between the Yamuna

and the Hindon is the Banganga which enters the

district from muzaffarnagar at village Dhanaura and ultimately meets Hindon at village Shahpur in Barnawa.

It sometimes dries up during the summer but gets filled up during the rany season.

1.2.7 Minor Streams

There are several other lines of drainage, the chief being as follows:

Abunala is one of the tributaries of the Kali nadi

(east) . It was converted into a channel in 1869 to bring the waters of the Hindon across the Ganga canal for irrigating Meerut. The attempt was not succesful and the section near Daulatpur was converted into an escape but this project was also abandoned and another 11 channel gani escape was made. From kapsarh to the east of Ganga canal, the nala is connected with a line of drainage which runs southwards by Pabli where it is joined by Alipur drain. The nala finally joins the Kali nadi (east) at village Kamalpur where it is known as

Khodan.

Kirthal drain with the help of its tributary the

Ramla, Mukandpur and Malakpur drains, the drian

carries of the rainy water of an area between the

eastern Yamuna canal and the nala distributary. The

general direction of flow is from north to south and it

falls into the Yamuna near Luhari . Kandhala drain

serves the area lying between the Kandhala distributary

on the west and the Yamuna canal of the east. It takes off from ponds near Kandhala town (in the district

Muzaffanagar) and flows north to south crossing the nala distributary. It drains off the area of villages

Lumb, Kakripur, Kirthal, Ramala and Budhpur (in chhaprauli block of Meerut district).

Alium drain takes off from the ponds of village

Alium (in district Muzaffarnagar) flowing north to south it falls into Hindon near village Asara in tehsil

Baghpat. Alwalpur drain is a tributary of the Yamuna and 12 gets its name from the village situated near eastern

Yamuna canal. The general direction of flow is from north to south. After flowing through the Yamuna khadar it falls into the Yamuna near Baghpat. It drains off the area occupied by villages of Angadpur, Alwalpur,

Ahmadpur, Bazidpur, Bijrol, Ban, Bichpari, Barka,

Barawadh, chhacharpur, Gorana, Gadhi, Naurozpur and

Sisna in tehsil Baghpat. 13

CHAPTER II

CLIMATE AND SOILS

2.0 The districts of Meerut and Ghaziabad experience a subtropical monsoon type of climate which is characterised by a seasonal rythem produced by the southwest and northeast monsoons. The reversal of the prevailing winds takes place regularly twice in a year.

The winds of continental origin blowing from November to middle of June are dry while in the other parts of the year, i.e. from mid June to October, they are oceanic in nature and are wet. On the basis of direction of the winds the year is divided into two seasons :

The season of northeast monsoons

The season of southwest monsoons

The direction of the winds in the region is generally from north-west to south-east during the north-east monsoon season and from south-east to north­ west during the southwest monsoon season. The season of southwest monsoon is commonly known as 'rainy season' and is characterised by cloudly weather, heavy rain fall and high relative humidity. The northeast monsoon remains dry barring few rainy spells on account of 14 western disturbences but is mainly characterised by- intense cold in some months and intense heat in the other. On the basis of these changes in rainfall and temperature, the Indian Metrological Department has divided the whole year into four seasons :

Cold weather season from December to February

Hot weather season from March to mid-June

Season of general rains from mid June to September

Season of retreating monsoon from October to

November

Common perople of Meerut and Ghaziabad districts, however, follow the agricultural calender which recognises three seasons corresponding with major agricultural activities.

1. Cold Weather Season (November to February)

2. Hot Weather Season (March to mid June)

3. Rainy Season (Mid June to October)

2.0.1 Cold Weather Season

This season corresponds to the period of rabi season. The crops of this season requires less water than those of the Kharif season. Due to low temperature on the surface, evaporation does not take place and it leads to low humidity of the air (Table I) . The air 15 Table I

Temperature and Relative Humidity in Meerut district

(1989-1990)

Temperature (°C)

Months Mean daily Mean daily Relative Maximum Minimum Humidity

January 21.15 6.31 86.90

february 22.86 9.05 76.68

March 27.98 12.44 68.22

April 36.49 19.42 49.83

May 40.11 24.25 39.80

June 36.42 25.21 61.80

July 30.74 26.20 85.80

August 31.10 24.51 86.00

September 23.38 23.77 62.60

October 31.70 15.70 72.58

November 26.72' 10.63 79.06

December 22 .01 8.80 83.06

Annual 29.22 17.19 71.02

Source: Memoirs of the Indian Meteroloqical Department. Vol VI, p. 195, 1990 IB

remains dry in this season. The season is rainless

except for a small amount of rain caused by the western

disturbences. The cloudly weather normally lasts a day

or so and is followed by clear skies1. During the

months of cold weather season the average number of

rainy days does not exceed more than two but whenever

.the damp cloudy weather persists, it produces various

plant diseases which have an adverse effect on the

crop. In the last month of the season with increasing

heat a strong local and thermal effect is added to the

western disturbences with the result that thunder

storms, hail storms and oceassionally tornadoes make

their appearences and bring some rains

The total amount of rainfall caused by the winter

depression is small. The rainfall is low, irregular and

sporadic. It is locally heavy where the thunder storms

are associated with disturbences. The rainy period is

also of short duration but the amount of rainfall

though small is highly beneficial to the winter crops

as it comes at a time when the plants are flowering

l Monthly and Annual Normals of Rainfall and Rainydays; Memoires of the Indian Meterological Department, VOL XXVII, part IV, Delhi 1949, p. 152 17

The effectiveness of the rainfall is further increased by the prevailing low temperatures. The hailstorms which sometimes occur in the area are of very limited duration and affect small and scattered areas. They cause little damage if covering at the early period of the cold weather season but a considerable damage is done to the crops when they occur at the time of the flowering of the crops and when the grains are immature. The area affected by this unfortunate natural disaster is very small and even with in this area the damage is far from uniform. Its affect varies enormously from field to field. One field may be seriously affected while the crop in the other on a short distance may escape almost untouched2. The month of February experiences a little change of weather except for a little increase in temperature.

2.0.2 The Hot Weather Season

With the gradual northward movement of the sun, temperature rise quickly and the atmospheric pressure falls over the heated land. The hot weather period extends from March to June. The rise of temperature in

2 Moreland, W.H., 'The Agriculture of United Province', Allahabad, 1912, p.29 18

March and clear skies with light westerly winds of the day and relatively cool nights produce good effect on the ripening of the rabi crops. In April the days are usually hot while nights remain still cool. The mean monthly relative humidity decreases to a considerable extent. The months of May and June record exceptionally high temparature while as may be as high as 40° and even more for a few days. (Table I & II) In hot season winds below from west, northwest to east and southeast.

In the months of May and June the hot winds known as

100 originate as a result of the convective air movement produced by the heating of the surface air and rapid decrease of temperature as one goes up in the atmosphere^ . Duststorms locally known as aandhis usually occur in the afternoons. These squally, blinding dusty winds are common phenomena in these regions.

2.0.3 The Season of General Rains

On account of excessive heat, a low pressure develops in northern part of India and by the middle of

June, it brings a complete reversal in the air

3 Blanford, H.F.,"Hot winds of north India; Memoirs of Indian Meteroloaical Department. VOL V, No.6, 1886, Calcutta, pp 162-195 19

Table II

Temperature and Relative Humidity of Ghaziabad district

(1989-•1990)

Months Mean daily Mean daily Relative Maximum Minimum Humidity <°C) (°C) (%)

January 20.8 8.2 82

February 23.5 9.8 68

March 28.8 15.0 55

April 36.3 20.3 40

May 40.6 25.3 38

June 39.8 28.5 56

July 35.2 26.9 78

August 32.6 25.5 83

September 33.8 24.6 79

October 32.9 18.3 68

November 28.9 10.9 63

December 23.9 8.0 75

Annual 31.70 18.30 68

Source: Memoirs of the Indian Meteroloaical Department. Vol. VII, p.180., 1990 20 movement. The winds begin to move from Indian ocean to the landmass. These humid oceanic southwesterly winds bring heavy downpours which reduce temperature of the area.

In the study area, the commencement of the monsoon rain varies from last week of May to first week of July but generally it sets in during the second or third week of June and continues till the end of October. The sudden arrival of monsoons transforms the whole landscape. July and August are the rainest months of the year and about 55 per cent of the total annual rainfall occurs during these months. The average rainfall is about 75 cms. The maximum and minimum temperature gradually falls from 39.80C0 and 28.50C0 in

June to about 35.2C0 and 26.9C0 in July as shown in

Figure 3. The relative humidity remains over 70 per cent throughout the rainy season.

This region receives rainfall from the Bay of

Bengal and Arabian Sea branches of southwest monsoon but by the time these branches reach the area they become somewhat weak and consequently rainfall of the district is relatively low and uncertain in comporison to eastern districts of Uttar Pradesh. Almost 90 per 21

MEERUT AND GHAZIABAD DISTRICTS TEMPERATURE AND HUMIDITY

MEERUT 50 -i100

45 - 90

40 - 80 • ¥->- u 35 • 70 a 0t u 3 a 30 • 60 *, •j> X <>- a 25 • 50 UJ UJ >H- a 20 • 40 < UJ 15 • 30 °V

10 • 20

5 • 10

0 —T— —r- -T— J o M M INOEX A MINIMUM TEMPERATURE MAXIMUM TEMPERATURE RELATIVE HUMIDITY GHAZIABAD

45

40

o 35 o UJ 30 a Z3 25

10

5

0

TEMPERATURE AND RELATIVE HUMIDITY OF MEERUT AND GHAZIABAD DrSTRICTS(l989-90)

SOURCE. INOIA METEOROLOGICAL DEPARTMENT

FIG-3 22 cent of the total annual rainfall is received during this season which is the most important season of the year from agricultural point of view. The reason receives on an average about 40 to 50 cms. of rainfall during this period. The rainfall is sporadic, short lived, subject to great local variation and frequently repeated about the some hours day after day for many days in succession. The distribution of rainfall is not uniform. It decreases gradually from northeast to southwest.

The rainfall in this region brings relief from the intense heat of the day and is helpful in the preparation of fields for sowing of Kharif crops but when winds are violent and are accompanied by clouds for more than two days with little rains they cause immense damage to the mango crop.

Monthly distribution of rainfall is not uniform throughout the season. Generally, rainfall starts by the third week of June, remains steady in July and

August and decreases in amount by September. The rainfall in the wet monsoon months decreases from east to west as well as from north to south. The westward decrease, however is not marked than the decrease 23 towards the south. The decrease of rainfall is not so high and well marked towards east to west but a significant decrease is found from north to south. The incidence of rainfall is not continuous throughout the season. Outburst of rain alternates with spells of fine weather which are very useful for the growing crops of the season. The spells of fine weather which do not last many days are produced by a shoulder of high pressure, embracing the whole area and pushing the axis of low pressure trough of Northern India towards the foot of the hills. Such a succession of intermittant rain and dry weather is most welcome to the farmers but if the rainless period exceeds ten or fifteen days, it may affect the kharif crops perticularly sugarcane adversely.

It is now needless to say that the rainfall in this area is unreliable during the months when its regularity is most needed. Such uncertainties in reinfall, espacially in the area where agriculture is reduced to more gamble with the monsoon due to the lack of irrigation facilities have an adverse affect on agriculture.

In September, the rain normally slacken and 24 rainless intervals become longer and day temperature begin to rise. The relative humidity remains as high as

78 per cent and the cloud amount decreases to 4 per cent. The low cloud amount, the long intervals between the rainydays, high humidity and high temperature, calm atmosphere with almost, motionless air make the month of September sultry.

In October, there is further decrease in the amount of rainfall but the mean maximun temperature remains as high as that in September. However, the humidity combined with an almost motionless air makes the months of September and October very opprasive and leads to the outbreak of a number of seasonal diseases.

2 .1 SOILS

The soils of the study area (Meerut and Ghaziabad districts) have been studing and classified by the

Revenue Department of the Government of Uttar Pradesh for revenue assessment purposes. A textural classification of these soil types in published in the

Settlement Reports and district Gazetteers of both

Meerut and Ghaziabad. Beisdes these, latest information on texture and chemical characterestics of soils was published in four volumes 'of Soil Survey and Soil works 25 in Uttar Pradesh in Allahabad. Usually the area under study is included into broad belt of alluvial soils without any further subclassification4. A textural classification of soils on the basis of colour, texture, availability of water and level of land has been attempted in these records.

The chemical soil of the region is classified on geological basis under two divisions; the new alluviam and the old alluviam, also known as Khadar and Bhangar respectively. Casual distribution between the two is some what difficult but usually the older deposits occupy higher lands and the newer deposits, the lower lands in the immediate neighbourhood of the rivers. The area under older deposits, however is much greater than that of the newer deposits.

2.1.1 Khadar or new alluvial Soils

The Khadar is sandy in composition and generally light in colour. It varies generally in texture from sand to silty sand. The Khadar land is found in narrow strips along the rivers Ganga, Yamuna, Hindon. The

Khadar of the Ganga and the Yamuna is sandy whereas the

4 D.N. Wadia, Krishnan, M.S. and Mukerjee, P.M., Soil map of the geological Survey of India, Memoirs of the geological Survey of India, 1935, Plate XXV 26

Hindon soil is silty sand. The Khadar of the Ganga,

Yamuna and Hindon attains its maximun width of about 4 kilometers. It varies in texture from gravel and sand in the upper courses to silt and silty clay in the lower courses of the rivers. During the period of heavy rains the ground get saturated and very often the sowing of rabi crops has to be deferred. Successive deposits of alluvial silt gradually raises the ground level till the land becomes entirely free from annual inundulation. At such places Khadar is extremely productive. The producitivity diminishes in places when the rivers take a sudden change in their courses owing to the accumulation of sand5•

The Khadar soil becomes almost dry in times of low rainfall and is heavily leached when the rainfall is heavy. The water fall in the Khadar lands is high and in the rainy season it comes close to the surface. The agriculture is not free from danger due to the water logging and floods. The sandy soil is utilized for the cultivation of maize, pulses and broadest rice in the kharif season while the sandy silt is used for the

5 Ray, chaudhary, S.P., Soils of India, Indian council of Agricultural Resarch, , 1963, pp, 385- 387 27 production of millets, barley, gram and lentil occupy

the largest area during the rabi season.

2.1.2 Bhangar soils

Bhangar or old alluviam is more clayey in

composition and generally dark in colour. On the basis

of texture, the Bhangar soils have been further

subdivided into the four divisions :

A Loamy

B Clayey loam

C Sandy loam

D Alkaline soils

2.1.2.1 Loamy Soils

It occupies a considerable area of Bhangar land.

Texturally, it is sandy loam and gradually changes to

silty clay, wherever the land is lowlying and is liable

to water logging the soils becomes clayey. The surface

soil is light yellow to brown in colour. It is rich in

organic matter. It has usually a high water holding

capacity and is capable of producing good crops if

irrigation facilities are available.

The soil is generally very fertile and is produces

a variety of crops. Generally, transplanted and broadcast rice, maize, millets, sugercane and kharif 28 pulses are grown in the kharif season, whereas wheat, barley, peas and gram are the dominent crops of the rabi season.

2.1.2.2 Clayey Loam

As compared to the loamy soil it is rich in clay and has a relatively high water retaining capacity. The soil is brownish in colour and in the lower horizons deepens to a dark grey in colour which is known locally as matiar. The soil is stiff and is of heavy in texture. This soil has a zone of kankar formation at lower depths. The soil below kankar is generally sandy and does not contain much clay. The calcium from the surface is leached and accumulates at various depths in the form of kankar nodules. The presence of kankar impedes the drainage with the result that during the rainy season water at places is head up and becomes stagnant.

This soil occurs in the central portion of the region stretching from north to south throughout the area. The proportion of clay decreases in high lying areas and the soil becomes loamy but in shallow depressions the soil is predominently clayey as the fine particles from the high lying areas are washed out 29 and get redeposited in these depressions. The soil in the low lying areas is best suited for the cultivation of transplanted rice.

In the northern tract of this soil the water table is high, the irrigation facilities are adequate but in the southern tract of this soil, the water table is relatively low. The tract therefore, produces good crops in kharif as well as in rabi season. Principal crops during the kharif season are sugarcane, maize and rice and in rabi season wheat, potato, barley, gram, peas and lantil occupy the largest area.

2.1.2.3 Sandy Loam

This soil occurs to the west of the loamy tract.

Texturally the soil is predominently sandy and the colour ranges from yellow through brown to reddish brown. It contains humus but lesser than loamy soils.

Without irrigation and manuring the soils becomes weak in crop production. The water holding capacity is generally low. The main crops grown in this soil are millets, pulses, maize, tobacco and groundnut in kharif and barley peas and potato is rabi season. Sugarcane also grow where irrigation facilities are available. 30 2.1.2.4 Alkaline Soils

The Saline or alkaline soils popularly known as reh. Usar are found scattered in vast stretches.

Usually these soils are found interspersed with agricultural lands. The main cause of their occurrence in the study region are attributed to the arid climate coupled with poor external and internal drainage of the area. The Himalyan rivers and their tributaries transport salts in solution which go on percolating into the soil of the plains. In those areas which suffer from low rainfall and have no proper surface drainage, these salts keep on accumulating by leaching from neighbouring regions. During the dry months the soluble salts are sucked up in solution by capillary action to the surface and are deposited there in the form of white af florescence. In this way the land having being impregnated with these salts are lost to agriculture. Soil scientists have made investigations and have suggested certain methods for improvement of drainage, use of organic manures, solution of salts tolerent crops and use of chemical substances. In this way the Usar land can be made useful for cultivation purposes. 31

CHAPTER III

AGRICULTURAL RESOURCES

3.0 Meerut and Ghaziabad have a large concentration

of large, medium and small scale industrial units and

still have great potential for further industrial

growth but agriculture continues to be the main source

of livelihood for its people. Agriculture provides

substance to about 69 per cent of the total population

living in rural areas and about 80 per cent of the

total area is devoted to cultivation. The general

utilization of land in the region for 1966-67 and 1990-

91 and the percentage of change occuring in this period

in Meerut and Ghaziabad districts is given in Table

III.

It will be seen from Table III that during the

study period from 1966-67 to 1990-91, the region

recorded an increase in land put to non agricultural uses (3.5 per cent), net cultivated area witnessed a

slight increase of 0.51 per cent, current follows and other follows o.83, 0.27 per cent respectively. All these additions were at the cost of barren and unculturable land which decreased by 1.30 per cent, land under miscellaneous trees by 0.45 per cent and 3^

f> H VO I I cnc in co CO -tf o o in CO CN 1 1 aj 0$ 1 vocn co rH o o o CN o o o 1 1 H CXiCT\ u + 1 + i + i + + + H H o 6M o\ o as o ^ CN in co in rH o o I O H CO CM vo CM H r*- 00 CM vo Cft in 1 CO en in VO in VO 00 •* H >* H

n EH O (TS o ^ o O CN O o H co o o r-.4J co in CO O H CO CO CN r> o •H iw O u •U V7\ co H O O CO vo CO H Xi CO O H in r~ cr> a\ N 05 4J o o H in H CN CO t> •* CN 9 id CD u CO co H co in CN H VO A U as VO CO o •d 0 id

3 to as QJ rH (V w (V 3

rH T3 ee s -H CO G n N •H SH as 4-) as 3 rH U •U oi tn 0) rH CD 3 3 rH o -0 n u X3 •a CD G i •H as c fl as as SH !H as a$ as CD •0 Cn 3 rH rH CO QJ U a 4J 01 id OS rH CD U as 1 rH -a CD r4 a) as c 3 o V 3 4J 01 Cn 0 u o co 4J to •o 5 c C C s -H CO as CD O CO •H id 3 £ as 5 •U rH 5 .U O T3 a as rH 0 iH •U -a S r-4 a) > as rH 0 a A a$ CD u rH •H 4-1 rH Q4 at •U a$ T3 C Xi U as cu 3 CO c (1) as rH U HH Pi a C a.) 3 a u 3 c u a) T3 £ JJ u CD as c u s-i C ft rH u u x: i .u m as 0 as d) 3 0) 3 aJ i 0 •J m tn J 04 U S u o EH 33 culturable wastes by 2.05 per cent. Thus, it becomes clear that more and more land has been devoted to non agricultural uses as a result of increasing population in harmony with increasing urbanization.

3.1 Irrigation

Among the basic determinents of agricultural productivity, adequate and timely availability of irrigation is the most crucial one. Under conditions of erratic monsoonal rain, non availability of irrigation becomes a limiting factor for the fruitful use of other technical inputs like improved seeds, fertilizers and farm power. By playing a protective as well- as productive role in the use of other agricultural inputs, irrigation becomes a catalytic agent enhancing the spread of green revolution, a symbol of agricultural devolopment.

Investment in irrigation forms a major past of the strategy of increased agricultural production and rural developmet in the successive fine year plan periods.

Traditional methods can not supply enough water and growing need of irrigation water has given rise to construction of canals and tubewells. Canal irrigation has played a vital role in making the region an area of 34 productive agriculture over the last two centuries.

Ground water has also played a crucial role in

agricultural transformation since the advent of high yielding variety of seeds. The introduction of high yielding varieties had made its imperative to establish

private sources of irrigation so as to provide timely

irrigation.

Due to the massive expension and intensive

utilization of irrigation facilities, Meerut and

Ghaziabad have made rapid strides in agriculture.

Irrigation has played an important role in icreasing

double cropped area yield of crops, intensity of

cropping and in changing cropping pattern from growing non- remunerative crops to remunerative ones. The

consumption of fertilizers, high yielding varieties of

seeds and extent of irrigated area has increased many

folds. Agriculture ecology had taken rapid strides with the application of water and has resulted in an appreciable increase in the crop yields.

During the decade 1961-71 the area experienced an important structural changes in its agricultural economy. There was a significant increase in the double cropped area and net. irrigated area. The region 35 witnessed a phenomenal increase in the number of tube-* wells and pumping sets and in the use of other scientific farm inputs and farm machinery. Agriculture has maintained its predominent position indicating the attraction exerted by it and its ability to provide reasonable standards of living. The planning for maximum returns from land based on the optimum utilization of the cultivated lands and the maintenance of agronomic balance among agriculture, forestry and grazing emphasize the need of a careful land use study in respect of it resource utilization pattern.

About 90 per cent of the total irrigated area is irrigated by canals or tubewells (Fig 4) . Inspite of the presense of canals, people prefer to use of tubewells because the farmer is faced with mismanegment and other difficulties in irrigation. Irrigation in

Meerut and Ghaziabad districts is provided through two different sources, firstly by channelising surface water from rivers and secondly by tapping subsoil water through wells, tubewells and pumps . The main source of irrigation in the region are canals, tubewells and other sources like wells and tanks . 36 37

3.1.1 The intensity of irrigation is a ratio between the gross irrigated and the net irrigated area1 during the period from 1960-61 to 1990-91 is given in Table IV.

Table /V

Intensity of irrigation in Meerut/Ghaziabad districts

1960-61 1965-66 1970-71 1975-76 1980-81 1985-86 1990-91

MEERUT 128.81 129.86 144.60 146.29 152.29 159.30 165.10

GHAZIABAD - - - 115.97 160.19 168.36

UTTAR PRADESH 108.83 110.17 116.06 117.93 120.01 122.96 125.15

The intensity of irrigation in the districts of

Meerut (165.10) and Ghaziabad (168.36) is much higher than the average intensity of irrigation in Uttar

Pradesh (125.15) in 1990-91.

Irrigation by different sources in Meerut district from 1966-67 to 1990-91 and the percentage of change is given in Table V.

1 The intensity of irrigation is calculated by the formula : Gross irrigated area Irrigation intensity index = x 100 Net irrigated area 38 Table V

Irrigation by different sources in Meerut district

1960-61 1990-91

Sources Area in Percentage Area in Percentage Percentage hactare from the hectare from the change total total 1960-61to 1990-91

Canals 173320 . 49.26 82175 31.43 -17.83

Tubewells 95488 27.14 176539 67.54 +40.40

Others 83038 23.60 2709 1.03 -22.57

Total 351846 100.00 261423 100.00 00.00

It will be seen from Table V that irrigation from tubewells has increased by 40 per cent is Meerut district during the thirty year period. The area irrigated by canals and other sources has, however, decreased by 17.83 per cent and 22.57 per cent respectively.

In Ghaziabad district, irrigation by different sources and percentage change during this period is given in Table VI.

In Ghaziabad district, tubewells are the main source of irrigation recording an increase of 19.55 per cent while canal and other sources of irrigation recorded a decrease of 8.08 per cent and 11.47 per cent respectively.

TABLE VI 3g

Irrigation by different sources in Ghaziabad district

1960-61 1990-91

Sources Area in Percentage Area in Percentage Percentage hactare from the hectare from the change total total 1960-61to

Canals 62200 38.44 54566 30.36 -08.08

Tubewells 78705 48.64 122544 68.19 +19.55

Others 20909 12.92 2605 1.45 -11.47

Total . 161814 100.00 179715 . 100.00 00.00

The aereal distribution of irrigation intensity as given in Table VII and Fig. 5 shows that very high irrigation intensity (205.0-218.3) is recorded in the southern part of the study area including the blocks of

Hapur, Razapur, Loni and Bhojpur.

High irrigation intensity (192.1-205.0) is recorded in Meerut, Dhaulana blocks which spread from north to south. Medium irrigation intensity (179.2 -

192.1) is recorded in Daurala and Khekra blocks. The areas of low irrigation intensity (166.3 -179.2) lie in the east to west and include the blocks of

Parrichatgarh, , Rajpura in the east and chhaprauli, Baraut, Baghpat and Pilana on the west of 40 41

Meerut district. The very low irrigation intensity blocks are seen from north to south namely, Sardhana,

Machhra, Kharkhauda, Mawana, Garhmukteshwar, Simbhaoli and Bisrakh.

3 .2 Crop land use

Agriculture and industries form the most important source of employment and revenue in the region. Kharif and rabi are the two main agricultural seasons. The

Kharif season corresponds with the summer and the major crops of this season are maize, millets, sugarcane, rice and pulses. The rabi season is generally confined to the winter months and the primary crops of this season are wheat, barley, peas, gram and pulses. The increasing pressure of population on land affects the agriculture in this area and agricultural lands are being used by expanding settllements. Most of the land is devoted to cash crops. The use of land from 1966-67 to 1990-91 and percentage change during this period is tabulated in Table VII.

It is clear from the Table VIII that with the development of irrigation facilities gross cropped area increased in the study region. The percentage share of gross cropped area to geographical area was 112.12 in 42 TABLE VII

Blockwise irrigation intensity in Meerut and Ghaziabad district in 1990-91

MEERUT DISTRICT GHAZIABAD DISTRICT

Blocks Intensity in % Blocks Intensity in %

Meerut 197.90 Garhmukteshwar 130.6

Jani 170.0 Simbhaoli 159.20

Rohta 178.0 Hapur 218.30

Rajpura 178.70 Bhojpur 204.20

Kharkhauda 160.20 Dhaulana 200.00

Mawana 153.40 Moradnagar 171.60

Hastinapur 167.50 Razapur 206.40

Parrichatgarh 176.50 Loni 218.00

Machhra 16C.20 Bisrakh 157.00

Sardhana 158.60 Dadri 178.70

Saroorpur 167 .30

Binoli 167 .30

Daurala 181 . 31

Baghpat 174 .30

Baraut 17C .2C

Chhaprauli 175 .OC

Khekra 182 .10

Pilana 173,.0 C 43 TABLE VIII

Crop Land-use in Meerut and Ghaziabad districts

1966-67 1990-91

Area in Percentage Aera in Percentage Percentage hectares from the hectares from the change Total Total

Net cultivated area 658510 76.30 501165 76.81 + 0.51

Area sown more than once 309283 35.84 325282 49.85 +14.08

Gross cropped area 967598 112.12 826447 126.66 +14.45

Kharif cropped area 515245 59.70 443169 67.92 + 8.22

Rabi cropped area 447147 51.81 336929 51.61 -0.17

Zaid cropped area 5079 0.58 46349 7.10 + 6.52 the study region in 1966-67 increased (14.45 per cent) in 1990-91. It has been observed that area sown more than once increased (14.01 per cent) as it was 35.84 per cent in 1966-67 and 49.85 per cent during 1990-91.

The percentage share of land under Kharif crop was highest in the study region during 1990-91. The percentage of share of land under rabi crops recorded decreased of 0.17 per cent during 1966-67 to 1990-91.

3.2.1 Intensity of cropping is closely related to irrigation because intensity of cultivation is higher 44 with the higher intensity of irrigation and it is lower with lower irrigation. Intensity of cropping, however, is invariably higher than the intensity of irrigation because double cropping is practised not only on irrigated land but also on unirrigated land.

TABLE IX

Intensity of cropping in Meerut and Ghaziabad districts (1960-61 to 1990-91)

1960-61 1965-66 1970-71 1975-76 1980-81 1985-86 1990-91

MEERUT 138.96 143.62 152.26 153.62 161.41 164.82 166.08

GHAZIABAD - - - - 160.08

Intensity of cropping indicates the extent to which land is used for agricultural purposes. It is a ratio between the gross cropped area and the net cultivated area usually expressed in per cent.

Intensity of cropping is a single indicator of the extent of multiple cropping on land under plough, that is the number of crops being raised in sequence in a year.

The index of intensity of cropping in Meerut district was 138.96 per cent in 1960-61 and increased to 166.08 per cent in 1990-91. Ghaziabad recorded a cropping intensity of 160.08 per cent in 1990-91. 45

The aerial distribution of cropping intensity is shown in Figure 6 and Table X reveals that very high cropping intensity (67.31-70.49) is recorded in

Sardhana, Hastin'apur, and Garhmukteshwar blocks which lie on the eastern side of the study area. High cropping intensity (64.17-67.31) is seen in

Parrichatgarh on the east, Daurala in the north, Hapur,

Razapur, Moradanagar lie on the south of the study region. Medium cropping intensity (61.03-64.17) blocks spreading from east to west including Mawana,

Saroorpur, Binoli, Chhaprauli, Baraut, Baghpat while

Dadri block lies in the south of the study region. The areas of low cropping intensity (57.89-61.03) including the blocks of Meerut, Jani, Rohta, Rajpura, Kharkhauda,

Bhojpur in the middle, Loni, Bisrakh and Simbhaoli lie on the south western side of the study area. Very low cropping intensity is recorded in Dhaulana block in the south, Khekra and Pilana on the western side of the study region.

3.3 Fertilizer consumption

Addition of plant nutrient in the form of fertilizer constitute an essential step in increasing agricultural producitivity. Fertilizer doses are 46 TABLE X

Intensity of cropping in Meerut/Ghaziabad district in 1990-91

MEERUT DISTRICT GHAZIABAD DISTRICT

Blocks Intensity in % Blocks Intensity in %

Meerut 58.53 Garhmukteshwar 67.93

Jani 59 .38 Simbhaoli 60.90

Rohta 60 .01 Hapur 65.93

Rajapura 59 .76 Bhojpur 59.54

Kharkhauda 60 .27 Dhaulana 54.75

Mawana 62..6 9 Moradnagar 65.60

Hastinapur 70..4 9 Razapur 65.34

Parrichatgarr. 65..6 4 Loni 60.25

Machhra 59..7 4 Bisrakh 60.76

Sardhana 68.,0 3 Dadri 62.89

Saroorpur 62. 50

Binoli 62. 70

Daurala 64. 06

Baghpat 62.86

Baraut 62.83

Chhaprauli 61.26

Khekra 57.69

Pilana 57.37 47

T" e JS T

"P:

1

> !r UJ •i cr 2 8 £ > 4S determined by crop variety, water availability, soil characteristics and management psactiees. The Indian soils in general were deficient in plant food materials and the need of the day is to solve this problem by suggesting suitable use of fertilizers by the farmers.

The addition of chemical fertilizers is thus a necessary step in increasing agricultural production.

Moreover, the adoption of high yielding variety seeds requires an adequate dose of chemical fertilizers because the soil reserves and its natural processes alone are not enough. The consumption of chemical fertilizer, therefore, has increased over the years particularly after the introduction of high yielding varieties in the mid sixtees. Table XI reveals the distribution of chemical fertilizers in kilograms in the study region of Meerut and Ghaziabad districts from

1970-71 to 1990-91.

Table XI reveals that district wise consumption of fertilizers has substantially increased in the study region Since 1970-71. Figure 7 reveals that out of 28 blocks of the study region, very high fertilizer consumption (192.82-232.60) is recorded in Meerut and

Hapur blocks of the study region. High fertilizer 49 TABLE XI 50

Use of chemical fertilizers (kg/ha.) in Meerut and Ghaziabad districts

1970-71 1980-81 1990-91

MEERUT 55.03 100.57 105.74

GHAZIABAD - 71.36 102.40

Source : Based on the data obtained from Agricultural Bulletin of Uttar-Pradesh, Directorate of Agriculture, Lucknow, U.P.

consumption (154.32-192.82) is recorded in Daurala block in the north and Simbhaoli and Bhojpur blocks in

the south of Ghaziabad district. Medium fertilizer

consumption (115.82-154.82) is seen in Mawana, Sardhana

and Saroorpur blocks in the north and Baghpat, Baraut,

Khekra and Pilana in the western part of the study-

region. The areas of low fertilizer consumption (77.32-

115.82) lie in the central and western blocks of the districts. The very low fertilizer consumption (38.50-

77.30) is recorded in the blocks of Hastinapur,

Dhaulana and Bisrakh spreading from north to south of

the study region. 51 TABLE XII

Fertilizer Consumption in Meerut and Ghaziabad districts in kg./bee. 1990-91

MEERUT DISTRICT GHAZIABAD DISTRICT

Blocks Intensity in % Blocks Intensity in %

Meerut 232.60 Garhmukteshwar 126..4 0

Jani 109.40 Simbhaoli 189..0 0

Rohta 102.40 Hapur 270 .50

Raj apura 76.20 Bhojpur 176..6 0

Kharkhauda 95.00 Dhaulana 63 .30

Mawana 151.50 Moradnagar 141..9 0

Hastinapur 73.70 Razapur 127..0 0

Parrichatgarh 88.90 Loni 86..7 0

Machhra 103.70 Bisrakh 38..5 0

Sardhana 129.00 Dadri 123..2 0

Saroorpur 123.30

Binoli 85.30

Daurala 164.40

Baghpat 126.20

Baraut 135.50

Chhaprauli 149.60

Khekra 144.70

Pilana 135.50 52

CHAPTER IV

HUMAN RESOURCES

4.0 Natural resource problems have recently been viewed more and more in terms of what they mean to people, indicating increased recognisition that the country's greatest resource in itself are people. The strength of the nation lies less in number than in quality, excellent health, high skills and effective institutional organisation taken together are fully as important as any of other factors of production and natural resources.

"Population is the pivotal element from which resource features drive their significance. It is, indeed, through an analysis of population features that an appreciation of regional differences can be fully made."1 According to Ginsberg, such a study is necessary for the correct understanding of social morphology2. _

Human resource is a factor of prime importance in the economic development of a region. Man in society

1 Trewartha, G.T., "A case for Population Geography", Annals for the Association of American Geographers. Vol.XLIII, No.2, June 1953, p.87 2 Spratt,W.J.H., Sociology. London, 1972 53 not only determines the economic pattern of resource utilization but is himself a very dynamic essential resource, providing the required labour and skill to plan and perform the process of utilization of natural resources.

In a study of human resources and its regionalisation, attention should be to focused on the analysis and pattern of population distribution, density, growth and literacy on regional or sub regional level. Table XIII shows economic classification of population of Meerut and Ghaziabad districts in 1991.

It is clear from the Table that the density of population with 1044 persons per sq. kilometer was much higher in Ghaziabad district than in Meerut district when it was 822 persons per sq. kms. in 1991. In

Ghaziabad district the percentage of urban population was much higher (46.41 per cent) than in Meerut district (37.10 per cent) in 1991. The percentage of cultivators to the total workers in Meerut was 32.71 while the percentage of workers to the total population was 27.46 per cent in 1991. 54 TABLE XIII

Economic classification of Population 1991

MEERUT GHAZIABAD

Total Population 3430398 2755494

Percentage of urban population to total population 37.10 46.41

Percentage of rural population to total population 60.77 65.87

Density of Population per sq. Jems. 822 1044

Percentage of workers to the total population 27.68 27.46

Percentage of cultivators to total workers 32.71 25.69

Percentage of agricultural labourers to total workers 18.92 12.34

Percentage of literate person to total, population 41.26 44.50

Source : Census Report, "Directorate of census operations, Uttar Pradesh, Lucknow, 1991.

4.0.1 Growth of Population

The growth of population between 1951-1991 is

given in Table XIV which clearly indicates an alarming

increase in population from 1951 onwards. 55 TABLE XIV

Growth of Population (1951-1991)

YEARS MEERUT DISTRICT GHAZIABAD DISTRICT

1951 1,540,065 8,55,577

1961 1,819,523 1,036,714

1971 2,207,957 1,340,902

1981 2,767,246 1,843,130

1991 3,43,098 27,55,494

4.0.2 Density of Population

Arithmatic density provides a view of real

pressure of population upon the resource base Table XV

and Figure 8 reveals that the density of population in

the study area is very high (591-683) in Meerut,

Rajpura, Daurala in the north, Hapur block in the south

and Razapur, Baraut on the western side. The areas of

high density of population (500-591) lie in a

continuous belt from north to south including Mawana,

Machhra, Simbhaoli, Sardhana, Saroorpur, Rohta, Jani,

Bhojpur, Dhaulana, Dadri, Chhaprauli, Baghpat, Binoli,

Pilana, Khekra and Moradnagar blocks. Medium density of population (409-500) was recorded in Kharkhauda block

of Meerut district while low density of population TABLE XV

Density of Population/100 sq.kms.

MEERUT DISTRICT GHAZIABAD DISTRICT

Meerut 616 Garhmukteshwar 374

Jani 589 Simbhaoli 581

Kohta 570 Hapur 598

Rajpura 662 Bhojpur 576

Kharkhauda 448 Dhaulana 502

Mawana 530 Moradnagar 501

Hastinapur 227 Razapur 608

Parrichatgarh 359 Loni 344

Machhra 531 Bisrakh 373

Sardhana 560 Dadri 520

Saroorpur 525

Binoli 553

Daurala 620

Baghpat 503

Baraut 683

Chhaprauli 545

Khekra 547

Pi1ana 547 57 58

(318-409) is seen in Parrichatgarh and Garhmukteshwar

on the east and Loni, Bisrakh blocks on the west of the

study area. Hastinapur block lying on the north-western

side of the study region has a very low density of population (227-318).

4.0.3 Literacy

Literacy is an important indicator of socio­

economic development of an area. It is essential for

social reconstruction, improvement in the quality of

life and preparation of man power for rapid development. Moreover, literacy works for moulding the younger generation to assume future responsibilities and develop appropriate value of life. On the other hand, lack of literacy can certainly be an impediment in the development process. A certain level of literacy is therefore, a basic requirement for people to get out of ignorance and backwardness.3 Literacy thus is essential for economic development and social advancement which measure over all development of a country.

Literacy rate is also an indicator of urbanisation

3 Gosal,G.S., "Literacy in India, An interpretative study", Rural Sociology, Vol.29,1964,p.26 59 in any particular region. The study are recorded 35.62 per cent literacy rate in Meerut district and 38.81 per cent in Ghaziabad district in 1991. An aerial distribution of literacy as presented in Table XVI and depicted in Fig.9 which indicate that very high percentage of literacy (29.45-30.71) is recorded in

Meerut, Mawana, Baghpat blocks of Meerut district,

Hapur and Razapur blocks of Ghaziabad district. The high percentage of literacy (28.20-29.45) blocks are

Daurala, Rohta, Sardhana, Binoli, Baraut in the north and Khekra, Loni, Moradnagar and Bhojpur on the south western side of the study area. Medium literacy (26.95-

28.20 per cent) is recorded in the areas, viz, Rajpura and Jani blocks in the middle, Garhmukteshwar,

Simbhaoli on the east and Bisrakh, Dadri, Dhaulana on the south of the study region. Low literacy percentage

(25.70-26.95) is seen in Hastinapur, Machhra on the east, chhaprauli and Pilana on the west. The very low literacy percentage (24.45-25.70) is recorded in

Parrichatgarh block of the east and Saroorpur block of the west. bo 61 TABLE XVI

Literacy in Meexnit and Ghaziabad districts 1981

MEERDT DISTRICT GHAZIABAD DISTRICT

Block Literacy in % Block Literacy in %

Meerut 29.92 Ga rhmukt e s hwa r 26.20

Jani 26.49 Simbhaoli 27.40

Rohta 29.00 Hapur 31.00

Rajpura 26.37 Bhojpur 28.00

Kharkhauda 25.08 Dhaulana 26.10

Mawana 30.71 Moradnagar 29.40

Hastinapur 25.78 Razapur 30.71

Parrichatgarh 24.95 Loni 29.10

Machhra 26.68 Bisrakh 26.30

Sardhana 29.23 Dadri 28.10

Saroorpur 24.45

Binoli 28.42

Daurala 28.71

Baghpat 30.82

Baraut 28.43

Chhaprauli 25.27

Khekra 28.67

Pilana 25.70 62

4.0.4 Distribution of Population

A cursory glance of the Table XVII and Figure 10 reveals that the distribution of population of the study area shows that very high concentration of population recorded in Hapur lying on the south-eastern side, Baraut on the western side of the study area.

Hastinapur block on the north western side and Loni on the east recorded very low concentration of population.

High concentration of population scattered in three areas i.e. Garhmukteshwar and Simbhaoli on the west,

Daurala in the north and Binoli, Pilana and Bisrakh on the western side of the study area. Medium concentration of population is recorded in Razapur,

Dhaulana and Dadri in the south, Mawana, Parrichatgarh,

Rajpura on the west and Saroorpur and chhaprauli on the north of the study region. The blocks of low concentration of population lying in a belt covering the blocks of Baghpat, Khekra, Loni, Rohta, Meerut,

Kharkhauda, Machhra, Hastinapur spreading from east to west of the study area.

4.1 Urbanization

Urbanisation is an important index of socio­ economic structure of a region as urban centres have 63 TABLE XVII

Distribution of Population (1981)

MEERUT DISTRICT 6HAZIABAD DISTRICT

Meerut 90811 Garhmukteshwar 125757

Jani 105148 Simbhaoli 127598

Rohta 96610 Hapur 186291

Rajpura 117994 Bhojpur 121056

Kharkhauda 88664 Dhaulana 114577

Mawana 103889 Moradnagar 95918

Hastinapur 75534 Razapur 113208

Parrichatgarh 111445 Loni 86634

Machhra 93590 Bisrakh 125574

Sardhana 97348 Dadri 117501

Saroorpur 100825

Binoli 148546

Daurala 148722

Baghpat 98372

Baraut 159446

Chhaprauli 100491

Khekra 87352

Pilana 118493 64

-J-

o- fM

Hi a. 2 o •k^

en oh- cr f- o co •.'/"• • • • • '••*• • •^ -• •^r~~ o < J. '. • •• • .1 •..i- •'.: • •' 6 .^u /•A -V X . •/. • • J: • • • " . > • • /• I r • • ^.- • • •// . • • •.••v< . •; r:-/- • / • • ••<• .V /, • . * • ^ CD • ' '• \ . \' •:>••• • -•^ ^ T^ •_ • . • a: • v" •• •:. • •" -Y >: \' •: ' /^>^^%/-( ' cr <"• V-., • •). O . ^/ • UJ , • ••> •r-'CV "\ • . <^- •// . J*; ui • _ • •'• s • 2 ,'-V J

z UJ to LU cr 1/1 Q. UJ o2 a CO o a. o UI O UJ o z o o fvi 6 c special role to play in its development. Urban centres being nodes of settlements are the real foci of social contacts and economic growth performing a number of important activities.

The urbanisation has transformed a large portion of agricultural land into built up area. The growth of settlement is reflected in terms of increase in size or area which is quantified in terms of amount of land specified for various urban uses e.g. residential, commercial, industrial, public or semi-public.

The expansion of urban land into formerly removal area espacially during the present century has caused the removal of numerous ecological habitats and the disruption of large numbers and wide variety of ecosystems.

Day by day, urban limits of cities are expanding.

Likewise, in the study region, Ghaziabad has grown from

5.34 sq. kms. in 1961 to 31.96 sq. kms. in 1971, 43.65 sq. kms. in 1981 and 72.02 sq. kms. in 1990-91. The population growth rate was 61.02 per cent in 1951-61,

81.7 per cent in 1961-71 and 124 per cent in 1971-81 which reflect that Ghaziabad in growing at an 66 extraordinary speed.'* The growth of Ghaiabad is generally towards Delhi and outwardly towards Meerut.

The growth of Ghaziabad is the result of pull force applied by the capital city Delhi. On the other hand,

Meerut has grown mainly in response to the needs of its agricultural hinter land and the city grew in the beginning mainly as a service centre and this function still continuous to persist as an important component of the urban economy. Around 1951, an important transformation took place when large number of refugees displaced from Pakistan, the tertiary sector of activities began to grow and the city has become an important trade and commerce centre. This marks the change from Urbanisation and commercialization.

Table XVIII reveals the percentage of urban population, its decennial growth rate, sex ratio by residents and density of population in 1991. It is clear from the Table XVIII that 46.41 per cent of urban population was residing in Ghaziabad in 1990-91 while

Meerut district contributes 37.10 per cent of that urban population of the region. In Ghaziabad district.

4 Singh, L., "Urban dynamics and Land use transformation; A case study of Ghaziabad; Town Planner •iournal . Vol. 9, No. 3, (45), Marah 1991, p.38 67 the density of population was much higher (1,044 persons/sq. kms.) than in Meerut district (822 persons/sq. kms.) in 1991.

TABLE XVIII

Percentage of urban population, decennial growth rate, sex ratio by residence & density

Urban popultlon Decennial Sex Ratio Density of as % of total growth rate (1991) population population of population per sg. Kms. % (1981-1991)

1981 1991 Total Rural Urban Total Rural Urban

1. Meerut 31.22 37.10 23.96 13.36 47.32 855 844 874 822

2. Ghaziabad 34.13 46.41 49.48 21.60 103.31 836 838 833 1044

4.1.1 Classification of towns

Beside Meerut and Ghaziabad cities there are a number of other medium and small towns in the study region. The total urban population of these towns is given in Table XIX and Table XX.

4.1.2 STANDARD URBAN AREAS

4.1.2.1 MEERUT

Meerut Urban area with a population of 846, 954 in

1991 is a class I city situated in the middle of Ganga

Yamuna Doab. It has been a class I city since 1901 68

TABLE XIX

Population of urban Agglomarates, cities and tovms in Meerut 1991

Towns/city/UA Population Growth rate 1991 1971-1981 1981-1991

1. .Meerut UA 846954 41.74 49.11 2. Meerut MC 752078 50.76 67.58 3. .Meerut Cantt. 94876 10.50 0.71 4. xBaraut MB 67673 48.07 46.19 5. Mawana MB 51644 51.34 37.28 6. Sardhana MB 42969 36.48 42.57 7. Khekra TA 35014 - 40.15 8. Baghpat MB 24918 47.07 45.24 9. Kithore TA 19279 . - 39.79 10. -Chhaprauli TA 15944 - 15.49 11. ^Hastinapur TA 15081 30.91 29.60 12. ^Rawar TA 14468 - 25.43 13. Sewalkhas TA 14400 - 40.11 14. TA 13955 - 35.13 15. Parichhatgarh TA 13675 - 20.72 16. --Tikri TA 12707 - 12.30 17. Shahjahanpur CT 12443 20.80 40.33 18. -Doghat TA 12310 - 22.87 19. TA 11040 - 11.57 20. Agarwalmand TA 10802 - 15.49 21. .Kharkhauda TA 10549 - 21.14 22. ' Daurala TA 9716 - - 23. Behsuma TA 8942 - 13.10 24. Aminagar Sarai TA 8249 21.29 20.65 69 TABLE XX Population of Urban Agglomarates in Ghaziabad district, cities/towns, 1991

Tovms /ci ty/UA Population Growth rate 1991 1971-1981 1981-1991

1. Ghaziabad UA Ghz 519508 109.56 80.91 A. Ghaziabad MB 460949 112.01 69.63 B. Razapur CT 47901 — 1072.61 C. Ghaziabad railway 10658 28.10 6.14 colony 2. Hapur MB 146591 44.30 42.55 3. Noida CP 167440 - - 4. Modinagar UA 124197 101.67 41.67 5. Modinagar MB 102307 79.99 30.76 6. Begumabad Budhana CT 13757 - 45.95 7. CT 8139 - - 8. Pilkhua MB 50218 58.24 32.56 9. Moradnagar MB 44442 86.25 70.62 10. Loni TA 36607 - 256.83 11., Dadri MB 32946 51.01 67.04 12. Hatahaj ipur CT 31355 - - 13. Garhmukteshwar MB 25258 63.79 41.00 14. TA 16388 - - 15. Pasaunda CT 12423 - - 16. TA 10922 20.89 19.81 17. Kalchina CT 10376 - - 18. Patala TA 9179 - 16.97 19. Niwadi TA 8866 - 25.26 20. Rori CT 8545 - - 21. Duj ana CT 7320 - - 22. Babugarh TA 3566 - 49.27 70 except for 1931 when due to decrease in population, it became a class II town. The population of Meerut recorded an increase of 49.11 per cent in 1981-91 as against 41.74 per cent during the proceeding decade

Table XXI

TABLE XXI

Standard Urban Area and Growth rate of population of core towns

Area in Population Growth rate sq.kms. 1991 1971-81 1981-91

Meerut 268.14 846954 41.74 49.11

Ghaziabad 515.49 519508 109.56 80.91

Hapur 86.24 146591 44.30 42.55

Modinagar 55.79 124197 101.67 41.67

The urban area has tended to grow towards the south west on Delhi road, south east on Garh road, in the south on Hapur road and in north on Sardhana road.

Meerut is an important industrial and commercial centre of western Uttar Pradesh.

The Urban component of Meerut Standard Urban Area consists of Meerut municipal board, Meerut cantonment,

Kankarkhera town area, Baskar Khera town area and

Abdullahpur town area while the rural component 71 consists of 3 villages of Sardhana tehsil and 64 villages of Meerut tehsil, Baskar Khera town area and

Adbullahpur town area have been treated as town for the first time in 1981. Malyana census town of 1971 has since merged in Meerut municipal board. Since 1971, villages Mustafabad, Bukarpur wholly merged in

Kankarkhera town area while villages Mohkampur,

Hafizabad, Maola, Medical college, Aarang Shahpur

Diggi, District jail and Nagla Bhatta, yadgarpur, merged in Meerut municipal board. The villages Nagla tehsil, Kasimpur, Khurampur and Dantal partly merged in

Kankarkhera town area. The villages Khuroli, Rampur,

Paoti, Ghosipur, Qazipur, Datauli, Jasupur and Rasna partly merged in Meerut municipal board and villages

Kasupur, Baskar partly merged in Baskar-khera town area.

4.1.2.2 Ghaziabad Urban Area

Ghaziabad Urban area has a population of 519508 in

1991. Being in close proximity to New Delhi, it has developed more or less as a sattelite town of the capital of the country. The population of the town has been increasing at a very rapid rate. In 1951, it was a class III town, in 1961, it became a class II and in 72 1971 a class I town. Its population during 1961-71 rose by 88.06 per cent during the last decade and the growth rate has further risen to 109.56 per cent with its population more than doubling itself. The growth rate was 80.91 per cent for the year 1981-91.

Ghaziabad, being a growing town, developmental activities are taking place in all directions. However, there are heavy concentration of these activities along the Bulandshahr road, Loni road and G.T. road. It is fastly growing into a major industrial and commercial centre. Even though, Hindon river is present as a constraint, the trans-Hindon area has also developed very fast due to the nearness of the town to the national capital.

Ghaziabad standard area consists of Ghaziabad municipal board, Razapur, including Kamla Nagar and

Shastri Nagar, Railway colony, Moradnagar municipal board, Moradnagar ordinance factory, Loni town area and

123 surrounding villages,92 of tehsil Ghaziabad and 31 of tehsil Dadri. Since 1971, a part of Loni village has been treated as a town area and the remaining portion as Loni rural. Village Dharauti Khurd has partly merged in Loni town area and the villages chak Ambapur, Karkar Mandan, Mehrajpur, Mavi, Mirzapur, Noornagar and

Dhargal have been wholly merged in Ghaziabad municipal board. Kaila of 1971 wholly merged in Ghaziabad municipal board and the village Paronda, jhandapur,

Sahibabad, Arthla, Pahladpur, Garhi and Mehrali have partly merged in Ghaziabad municipal board.

4.1.2.3 M0DINA6AR

Modinagar Urban Area of Ghaziabad district has a population of 124197 in 1991. It has become a class I town for the first time in 1991. It is the largest township in the upper Ganga Yamuna Doab and an important market centre serving a large hinterland.

Being a township of a leading and expanding industrial organisation, the population of the town is increasing at a very fast rate. The rate of growth during the last three decades has been 97.22 per cent in 1951-61, 79.14 per cent in 1961-71, 101.67 per cent in 1971-81, while it was 41.67 per cent for 1981-1991.

The town is mostly expanding in the north east and south west directions along the Delhi-Meerut road. It is now tending to grow towards the south east along the

Hapur road.

Modinagar Standard Urban Area comprises Modinagar 74

M.B., Begumabad Budhana, CT and 15 villages of tehsil

Ghaziabad on the periphery of the town. Begumabad

village, a rural component of the standard Urban Area

in 1971 has since formed Begumabad Budhana census town

in 1981.

4.1.2.4 HAPUR

Hapur, a municipal board of Ghaziabad district has

a population of 146591 in 1991. In 1971, Hapur was a

class II town but became class I town in 1981. The rate

of growth of population of the town during the decade

1971-1981 was 44.30 per cent as against 28.99 per cent during 1961-71. The rate of growth of population was

42.55 per cent during 1981-1991. Hapur is an important mandi for foodgrains on the Delhi-Moradabad national highway and the Bulandshahr-Meerut road. The expansion of the town is hindered by the presence of chijja Nala and the Kalinadi. Hapur municipal board, Babugarh town area and 23 neighbouring villages including 19 villages of Hapur tehsil and 4 villages of Meerut tehsil of

Meerut district constitute the Hapur standard urban area. Since 1976, the villages chamri, Hapur rural and

Arsura have partly merged in Hapur municipal board. The villages Babugarh, state machenised from Babugarh and 75 TABLE XXII

Persons engaged in non-agricultural activities (%)

Meerut district Ghaziedsad district

Blocks Blocks

Meerut 8.87 Garhmukteshwar 5.84

Jani 6.11 Simbhaoli 6.10

Rohta 4.40 Hapur 5.42

Rajpura 7.27 Bhojpur 5.39

Kharkhauda 3.11 Dhaulana 4.93

Mawana 4.88 Moradnagar 5.91

Hastinapur 4.53 Rajpura 8.83

Parrichatgarh 4.72 Loni 3.22

Machhra 4.12 Bisrakh 3.44

Sardhana 6.13 Dadri 3.07

Saroorpur 5.07

Binoli 6.56

Daurala 6.64

Baghpat 4.39

Baraut 5.56

Chhaprauli 5.62

Khekra 5.94

Pilana 6.04 76

Central Potato Farm have together formed Begumabad town

area in 1981.

4.1.3 Persons engaged in Non-Agricultural Activities

The population engaged in non-agricultural

pursuits in various blocks of the region are also an

indicator of urbanisation. A cursory glance of Table

XXII reveals that in Meerut district population engaged

in non-agricultural pursuits ranges from a minium of

3.11 per cent in Kharkhauda block to maximum of 8.87

per cent in Meerut block. In Ghaziabad district, this

range lies between 3.07 per cent in Dadri block and

8.03 per cent in Rajpur block. Amongst the other blocks

of the two districts Razpura, Daurala, Binoli and

Simbhaoli had 6.55-7.71 per cent population engaged in non-agricultural persuits while Sardhana, chhaprauli,

Baraut, Khekra, Pilana, Moradnagar, Bhojpur, Hapur and

Garhmukteshwar blocks had 5.3 9 - 6.55 per cent and

Hastinapur, Parrichatgarh, Machhra, Rohta, Saroorpur,

Baghpat, Dhaulana, Loni, Bisrakh and Machhra blocks with figures between 5.39 and 3.07 had low percentage of population engaged in non-agricultural activities. PART II INDUSTRIAL BASE CHAPTER V

INDUSTRIAL DEVELOPMENT

5.0 The economy of Uttar Pradesh is basically agrarian

in nature. However, if an all round development is to

be achieved then even in . an agranian economy, the

importance of the industrial sector cannot be

undermined. Agricultural development itself depends on

industrial development as industry provides many key

inputs which facilitate agricultural development.

Similarly, various industries also use a variety of

agricultural products as their key inputs. Above all,

agriculture alone cannot solve the problem of the masses. Land being a fixed asset, it can provide

employment only to a limited extent. Industrial

development is therefore, essential if full employment

is to be achieved. Industrial production therefore, needs to be stepped up for 'i«fnproving fh'd standards of

I -K |V( living of the masses. '* < fS- ^j ^^ / ^ "

Agriculture and industry .are.-identified as the main components of the productive base of the economy.

This does not however, underrate the importance of the

third component of the economy viz, services. Indeed the role of services increases with economic progress. The function of services essential for the growth and maintenance of economic activity. Therefore, the relationship between agriculture and industry is that of interdependence and is complementary.

The state of Uttar Pradesh continues to be industrially backward both in relative and absolute sense. The industrial backwardness of Uttar Pradesh is revealed by the fact that in 1981-82 it accounted for only 10.31 per cent of India's total factory employment and 7.55 per cent of the total factory output as against more than 16 per cent share of the state in

India's total population. Moreover, industrial activity is very unevenly distributed within the state itself.

The western region claims about half of the aggregate industrial activity in the state while the central and eastern region each account for about one fourth to one third of it. The share of the Bundelkhand and Hill region in different industrial aggregates on the other side continues to be very low.

In 1961, the state had a total of 1064 registered factories of which one half were located in western region alone. The central region accounted for almost 79 another one fourth units and therefore, the remaining three regions had barely 20 per cent of the total units located in them. It is therefore, evident that considerable disparities existed among the different regions and there was a heavy concentration of industrial activity in two regions of the state. The situation was worse at the inter district level. Four districts namely, Agra, Meerut, Ghaziabad and Kanpur taken together accounted for almost half of the total factories. In 1971, the total number of units had gone up to 3649 however, their distribution across the regions remained more or less unaffected. The four industrially advanced districts continued to be the dominant centres of industrial activity despite the fact that their share of total factories had declined to around 46 per cent. During this period 48 districts got registered factories. Some other districts also began to emerge as important from the point of industrial location. Even during the next 10 years, a fast growth was observed in the total number of units and their number stood at 5540 in 1980-81. The share of western region, which had declined marginally in 1971 went up around 61 per cent. 80

Regarding the growth of industries, from the point

of view of employment generation, it is seen that in

1960-61 the registered factories provided employment to

around 1.78 Lakh persons. Although the western region

had over half of the total units, its contribution to

employment was only around 40 per cent. The units of

the central region provided employment to another 40 per cent workers, although its share to total units was

less than one fourth. This is primarily due to the fact that the cotton textile units of Kanpur had a very high

share in employment. They in fact, accounted for two third of the total employment in the factories of the central region.

The increase in employment between 1960-61 and

1970-71 was commensurate with the increase in total units during the same period. Employment continued to keep pace with the growth of industrial units and thus by 1980-81, total employment stood at 6.08 Lakh workers. The western region continued to have the highest share in employment.

Despite the fact that there was a considerable increase in the total units as well as output and 81 employment in the registered factories, the share of the manufacturing sector to the total output from commodity producing sectors showed only a small increase from 11.5 per cent in 1960-61 to 18.5 per cent in 1980-81, it proves that even as late as 1980-81, the manufacturing sector has been playing only a secondary role as compared to agriculture.

In 1961, two industry groups, viz. food products and textiles taken together accounted for around 50 per cent of the total units and 78 per cent of the total employment. Both of these industry groups were raw material based and as it could be expected in an agrarian economy, industrial activity centered around these industries.

By 1971, various other industrial groups began to emerge which were not raw material based with the result the dominance of the food products and cotton textile units automatically had a sharp decline and their share in total units as well as in employment went down to 31.66 and 43.11 per cent. The new industry group that were emerged were paper and paper-products, chemicals, non-metallic mineral products, basic metals and alloys and the machine tools units. These together 82 accounted for around 36.75 per cent units and 24 per cent employment. These industries were located in those districts which were industrially backward.

During the period 1971 to 1981 the state witnessed a considerable growth of the new industry group that had emerged as significant in 1971. Paper and paper products units had an increase of around 21.5 per cent.

The non-metallic mineral groups of industries had a more than two fold increase during this period.

Similarly, there was considerable increase in the case of basic metals and alloys, as well as in units manufacturing metal products, machine tools and electrical machinery. The increase in employment was found in non-metallic mineral products, basic metals and alloys and electrical machinery manufacturing units. However, the food products group of industries continued to remain the single most important industry group in terms of units and employment both. Thus it is clear, that in the two decades beginning from 1961 to

1981 the state witnessed a substantial growth not only in the number of industries and the level of employment but also went through a shift in the industrial 83 structure. The emergence of the footloose type of industries added a new dimension in the industrial development of the region.

In the study region, Meerut city demographic growth was characterised by the slow growth till 1931 and sudden spurt between 1941 to 1951 a tendency to slow down during the next decade and again a rising trend since 1961. The sudden spurt between 1941 and

1951 was caused mainly by the influx of immigrant refugees from Pakistan, following the country's independence, while the tendency for growth exhibited during 1961-71 may be attributed to the structural changes taking place in the country's economic base.

The situation of Ghaziabad in close proximity to

Delhi, coupled with the partition of the country in

1947, acted as the greatest stimulant for the rapid growth of industries in the city. Influx of refugees in large number into and around Delhi posed the problem of unemployment on a massive scale in the capital .

Ghaziabad because of its nearness to Delhi started attracting the attention of private entrepreneurs coming from Pakistan and gradually a number of small and medium sized industrial units sprang up in the city 84 during the early post independence years. Setting of

Ghaziabad Improvement Trust and the introduction of

'Ghaziabad Master Plan' around 1960 further paved the way for rapid industrialisation.

Phenomenal growth of industries at Ghaziabad during the recent past has attracted the attention of all interested in Industrial geography. During the past three decades (1951-1981) the number of registered fortories and employment figures have shot up to 452 and 37731 in 1981 from the corresponding figures of 30 and 2555 in 1951. The spectacular growth of industries makes it pertinent to enquire as to why and how

Ghaziabad experienced such an accelerated rate of industrial growth during post independence period only when the nucleus of the city had been laid down as early as 1740. Ghaziabad does not signify a town which can be called a creation of industrial revolution.

Industrial growth started here 200 years after its inception, while at the other old cities of India, modern industrial activity had commenced quiet earlier.

Meerut and Ghaziabad districts were predominately an agricultural one in the past and manufacturing did 85 not occupy a significant place in its occupational pattern. Nevertheless, certain industries did exist in the 19th and in the early 20th century which call for special mention as they gave employment to large number of persons, the chief being the leather industry which was found to be fairly remunerative one. Tanning of hides was done on a large scale. Hide, hooves were sent to Calcutta and Kanpur. Shoes manufactured by hand at

Pilkhuwa were mostly exported to the neighbouring districts and Delhi. To a considerable extent foot wares were also manufactured at Ghaziabad, Muqimpur and

Hapur.

The region were also cotton producing area and therefore, a big centre of cotton trade and cotton weaving developed here. More than half of its cotton output used to be exported to Calcutta and Bombay till about the close of 19th century and some of it was sent to Kanpur at the beginning of the present century. The rest was utilised in the area itself. A good deal of cotton printing was done at Barnawa, blankets are manufactured at Miranpur in Sardhana tehsil of Meerut district. Jawalagarh in Sardhana and in Daurala were the two other places where ordinary blankets were S6 used to be made of wool chiefly imported from Punjab.

At the beginning of the century the silk industry was

also of some importance in the study region. This

industry gave rise to an ancillary operation of

embroidery silk. The pottery industry which goes back

to 18th century appears to have been introduced into

the region from Multan and in style the ware once

closely resembled the products of that place. The

cultivation of indigo and the manufacture of dye in

this region goes back to pre-British times, the latter being generally in the hands of muslim landholders but when Bengal fail to supply indigo, the industry in the region had a revival probably through the efforts of the skinner family who established a factory at Dehra

(in Ghaziabad). By that year, some other factories had began to work in Ghaziabad, Baghpat, Hapur but by the beginning of the present century the industry had almost disappeared. Since the 19th century glass bangles have been manufactured in Daulatpur and Panchi

(in Baghpat), iron vessels of various kinds were made at Baraut, belts and brassware at Hapur. At one time the village of Sikhohpur in Ghaziabad was famous for 87 the ornamental elephant goods but this industry languished owing to the dearth of demand.

5 .1 Geographical bases

Meerut and Ghaziabad districts offer an optimum condition for the location of all types of manufacturing activities. Main part of Ghaziabad city lies to the east of river Hindon. This portion contains some of the most developed industrial units of the city with the exception of a narrow belt of land along both the sides of the river Hindon, which are suceptible to floods during rainy season, all other areas of the city can be safely used for industrial establishments. Not only relief but the local geology of the area which comprises of thick and fine grained alluviam also support the cause of industrial activity.

Thus, availability of large tracts of level lands along the major highways and also along the regional level roads passing through the city is a big boost in promoting the industrial development in the city. In order to properly understand the vast' industrial structure of Ghaziabad keeping into past assumes even more significance because of the great role played by inter-industry linkages in furthering the cause of 88

industrial development in the city.

On the other hand, Meerut district is located in

an agriculturally productive area which is one of the most active development corridors around Delhi with

close linkages to the national capital and to the

industrial centres in its vicinity. Meerut has grown mainly in response to the felt needs of its

agricultural hinterland and it is the later which has been feeding and sustaining its growth. The city grew

in the beginning mainly as a service centre and this

function still continues to persist as an important

component of the urban economy. Around 1951, an

important transformation took place when with the in- migration of a large number of refugees displaced from

Pakistan, the tertiary sector of activities began to grow and it become an important trade and commercial centre too.

5.1.1 Climate

Though, there are very few industries which are directly affected by prevailing climate of a place, indirectly climate exerts substantial influence on all types of manufacturing. Extremes of cold or heat and 89 excessive dryness or humidity produce negative effects on the industrial productivity.

5.1.2 Raw-material

The importance of raw material in deciding the geographical location of the industry has been considerably reduce due to the development of modern means of swift and efficient transport. Nearness of raw-materials exerts an influence in the location of industries only in case of those who use perishable weight losing raw material, on the whole, the vast and varied industrial structure of the region depicts very little relevance to the local raw material base. Almost

70 per cent of the raw material is obtained from distant places of Bihar. The only raw material obtained from local sources and from Delhi^metropolitan area is scrap which is used by mini steel making centres of the region for making special types of steel. Raw materials which is obtained from distant sources includes cotton, tobacco, apple, pulp, non-metallic minerals, chemicals, rubber and medicinal herbs. The only raw material which are obtained from nearby areas are oilseeds and vegetables, waste paper and scrap iron. 5.1.3 Transportation ^"

No doubt, the greatest resource of the region lies in it situation at the junction of important routes coming from Delhi, Calcutta, Dehradun and Moradabad. A high degree of nodality of the region in respect of its surrounding areas is further reinforced by its proximity to the capital region of Delhi through which it is connected with all the other parts of the country. The region stands as a gateway to Delhi for all parts of Uttar Pradesh, Bihar, West Bengal, Assam and other eastern states (Figure 11).

5.1.4 Population

Availability of labour which is of paramount importance for all sorts of manufacturing is closely linked with the density of population over a place and its surrounding areas. Labour characterise a mobile factor but unskilled labour is relatively much less mobile and hence a pre-existing population over an area offers a definite advantage in respect of labour supply.

On the whole, demographic characteristic of the city are conducive to the industrial climate prevailing in the city. The vast pool,of population in the cities 91 92

and adjoining areas ensure an adequate supply of both

skilled and unskilled labour. Prosperous agriculture in

the surrounding region provides for the regular and

adequate food supplies for the industrial population.

The labour relation in the region have not yet hardened

to the extent as those in other old established

industrial towns of the country and this necessarily

serves as an additional advantage in respect of labour

supply for starting a new industry. CHAPTER VI ^ *^

INDUSTRIES : TYPES AND DISTRIBUTION

6.0 LARGE SCALE INDUSTRIES

The study region had some industrial importance in the state for the last 30 years. A large number of units were established here by displaced persons who came to this region at the time of the partition of the country. The diversified and rapid development of small scale and other industries in the region has been appreciable after the attainment of independence in

1947. The region has a number of large and medium scale industries like sugar, distillery, chemical works, metal products, agricultural implements, sports goods and handloom. Important industrial focal points of the region are Ghaziabad, Noida, , Dadri,

Modinagar, Hapur, Daurala, Mawana, Modipuram and Meerut itself in addition to the other industrial units dotted all over the region.

A variety of commodity are manufactured in the study region and a brief historical account of important commodities are given below.

Sugar : The region did not have any sugar mill till

1932 when two sugar mills, the Daurala Sugar mill, 94

Daurala and Jaswant Sugar Mill, Meerut were established. Three more, Simbhaoli Sugar works,

Simbhaoli, Modi Sugar works and general mills (Private

Ltd.), Diwannagar were set up in 1933 and two year later, one more the Ramlakshman Sugar mill,

Mohiuddinpur was established. One of the reason of these factories coming into being was the grant of protection by the Indian tariff Board to the sugar industry. As a result of the fixation of the quota of sugar production in the year 1940-41, further expansion of the industry was not possible during the second world war. After independence, with more production of cane, two more sugar factories were established, the

Mawana Sugar mills in Mawana in 1949 and the Baghpat co-operative sugar mills Pvt. Ltd. in Baghpat in 1956.

Vanaspati Oil : There were three vanaspati (Vegetable) oil factories in the region, two at Ghaziabad

(Hindustan Lever Ltd. and Amrit Vanaspati) and one at

Modinagar (Modi Vanaspati manufacturing Company). The capital invested in these factories in 1960 was Rs.

130,12,945 and the value of the raw material used was

Rs. 9,27,74,428. The oil for the industry is imported 95 from Punjab, Bombay, Delhi, Madhya Pradesh, Mysore and from within the state itself.

Cloth : The Modi spinning and weaving mills and company and the weaving and Bottling factory (Pvt.

Ltd.), Ghaziabad were the two large scale cloth mills of the region. The capital invested in these mills in

1960 amounted to Rs. 1,38,06,420 and they employed 5057 individuals and produced cloth of the value of Rs.

547,13,830.

Oil : Of the two large scale oil expeller factories in the region. One is located at Modinagar and the other at Hapur. The former or the Modi mills has 26 expellers and 112 kolhus and used mustard ground nuts, mahua and neem which are purchased locally. The later, The Tara oil and ginning mills (established in 1932) produces mostly mustard oil and ground nut oil . The amount invested in these factories in 1956 was Rs. 30,37,000 and they employed on an average 397 persons daily. The product was valued at Rs. 1,67,74,300 in that year.

Spirit and chemicals The three large scale distilleries and chemical factories of the region were located, at Modinagar, Meerut and Simbhaoli and produce power alcohol, rectified spirit and denatured spirit, 96 the products being valued, at Rs. 21,73,588 in 1960.

These concerns had a capital investment of Rs.

30,45,645 in that year.

Paper : There were three paper mills in the region. The

Meerut straw board mill, Meerut is located on the

Meerut Baghpat road. In 1960, the capital invested in it was Rs. 25,80,000 and it employed 430 persons, the product being valued at Rs. 41,55,000. The Swatantra

Bharat paper mills, Pilkhua, has a capital investment of Rs. 10,00,000 paper worth Rs. 38,00,000 was produced in 1960-61, when 46 people were employed. The national

Abrasive works Ghaziabad has a capital investment of

Rs. 8,00,000. It produced paper worth Rs. 6,62,000 in

1960-61 employed 48 persons. lantezTLS : The Modi Lantern works, Modinagar came into existence in January, 1950. The capital investment in

1960 was Rs. 13,70,000 and the Lanterns produced were valued at Rs. 24,88,033. The factory is equipped with modern machinery and lanterns of different sizes and varieties are produced here.

Paints and Varnish The Modi paints and varnish manufactures several types of paints and varnish. In 97 I960, the capital invested in the mill was Rs. 6,95,000 and it employed 95 persons and produced good valued at

Rs. 20,00,000.

Flour : The Kishan flour mill is situated in Meerut city and was started in 1921 as a private enterprise.

The capital investment was Rs. 12,00,000 in 1956 and 70 persons were employed in the industry in 1960.

Bone Products : There were two large scale mills both at Hapur which produce bone products, the R.K. Galetine and Bone mill and the Hapur bone mill. The former established in 1942 had a capital investment of Rs.

10,00,000 in 1956 and products crushed bone, bone grist, bone meal and glue. In 1956, both the mills produced crushed bone and bone grist, bone meal, bone cynuse and glue valued at Rs. 25,78,500 and employed

143 persons.

Engineering Equipments and Apparatus The large scale works which produced engineering equipment and apparatus are Guru Nanak Engineering company. Modern

Industries, Sahibabad, Delhi Iron and steel company all in Ghaziabad. In 1960, the total capital investment of these factories stood at Rs. 54,45,904 their products were valued at about Rs. 1,40,00,000 and they employed

911 person. 93 Soap : The Modi Soap works, Modinagar (established in

1940) had a capital investment of Rs. 14,25,000 in

1956, when it employed 186 persons. The mill produced goods valued at Rs . 11,52,684 in 1960, the chief

articles produced being washing soaps, toilet soaps and

glycerine soap.

Musical Instruments : The firm of Nadir Ali and

company, Meerut is the premier producer in northern

India, of musical instruments like trumpets, cornets,

clarionets, trombones, bugles, brass drums etc. It was

started in 1885 when it only imported instruments used

in brass bands but it started manufacturing such

instruments in 1927.

Irrigation Workshop : The irrigation workshop of Uttar

Pradesh Government is situated on the Meerut Mawana

road. It was started in 1949, it produces equipments

for the use of Govt, and has a machine shop, a fitting

shop, a foundry shop. It manufacture various types of

sluice and damgates, fabricates, steels, structures and transmission towers, tubewell pumps, pipes for water works, heavy road and steelbridges and undertakes repairs of compressors centrifugal pump and impellers. 99 Small scale Industries : At the end of the 1960, there

were 1,173 small scale industrial units in the region

having a capital investment of Rs. 528 crores and

providing employment to about 20,000 workers. The

development of these industries is being undertaken by

means of financial existence given by the government,

distribution of raw materials at reasonable rates,

marketing and quality control, technical supervision

and facility for hire and purchase of equipments.

Sports goods : The biggest industry of Meerut city is

the sports goods industry, which has developed

considerably since 1947, when many displaced persons

mostly hailing from Sialkot and who were concerned with

the manufactured of sport goods there settled down in

Meerut where they started making sport goods.

Government offers monetary and other facilities to

these person for this purpose and at one tine, the number of organisations engaged in the manufactured of

such goods went upto 130. The material used in the manufacture of cricket bats, cricket balls and shuttle

cocks are imported from United States and france.

Cutlery : The industry for the • manufacture of Seissors, razors and batel nuts crackers is the oldest in the 100 region. The Seissors industry is about 90 years old. It was first started by a dexterous blacksmith, Muhammad

Akhoon. He was able to produce three to four pairs of

seissors of good quality in a day. His method was copied and gradually the industry grew as did its reputation. After the second world war, it had to face a stiff competition from seissors manufactured in other parts of India and abroad but with the assistance provided by the Government, heat treatment workshop which was established particularly for this industry,

it is now regaining lost ground.

Engineering Equipments : The important feature of this industry is the manufacture of spare parts for Sugar mills machinery. Engineering works are spread all over the region some of the units being engaged in the casting of metals.

Agricultural Implements The study region is agriculturally developed districts of the state and is also an important place for the manufacture of agricultural implements. In 1960, there were at least twelve units that were producing agricultural implements in the region many kinds of being turned 101 out. Besides these, small scale units others like metal goods, electrical wires, cycles, ice and cold storages, gur and khandsari, flour and dal, calendering also important in the region, while in the category of village and cottage industries Handloom clothes and khadi-leather tanning and shoe making, jaggery, kolhu oil are also important.

Industrial estates and Areas : Ghaziabad has taken great industrial strides during the last fifteen years.

The central and the state government have evinced some concern over the rather haphazard development that has taken place and the consequent speculation in land prices. The state government published the draft master plan for the regulated area of Ghaziabad in 1960. This area is divided into three parts that is and around the municipal limits of Ghaziabad, the area of both sides of the grand-trunk-road from the river Hindon to the

Delhi-U.P. Border and the area on both sides of

Shahdra-Saharanpur road from Delhi-U.P. border to about

3.2 kms . beyond the flood control band near Loni .

Adequate areas have been reserved for heavy industries on both sides of the grand-trunk-road on way to 102

Bulandshahr, south of the railway station of Ghaziabad

and south of the railway station of Sahibabad as far as

the proposed road connecting Uttar Pradesh with Delhi.

Sites have also been reserved for light industries east

of Meerut road, on both sides of the grand-trunk-road.

A rural industrial estate has been established at

Loni in Ghaziabad and basic facilities like electric

power, water supply and adequate raw materials have

been provided. The work inconnection with the

establishment of three industrial estates in Meerut

district and two others in Hapur and Ghaziabad has also

been taken. An industrial estate for the production of

sport goods at Meerut is also being setup. Two other

important industrial townships in these districts are

those at Modinagar and Mohannagar. The former is the venue of the Modi group of industries and the latter is

concerned with the manufacture of malt extract and brewers yeast.

6.1 An attempt has been made to study the process of

industrialisation in the study area by using three

indicators, number of registered units, employment and production according to the latest available figure for 103

1990-91 published by 'District Industries centre of

Meerut and Ghaziabad districts.

Large and medium scale units contribute a lot in the industrial development of Meerut and Ghaziabad districts. It is clear from the Table XXIII & XXIV that highest number of registered units are established at

Razapur (141), Bisrakh (23), blocks followed by Dadri

(21), Bhojpur (14) and Loni (9). Simbhaoli, Daurala,

Baghpat have 2 units in each blocks while the remaining blocks namely, Mawana, Hastinapur, Sardhana, Baraut,

Hapur have one unit in each block of the study region.

Highest employment in these units recorded in

Razapur block (35958) followed by Loni (3273), Bhojpur

(6450), Simbhaoli (1715), Daurala (1270), Meerut

(13188), Baghpat (1095), Mawana (598), Hastinapur

(1010) and Baraut (800),

Thus it is clear that highest concentration of large and medium units are mainly confined to Razapur,

Meerut, Bisrakh, Dadri and Loni blocks of the study region. These are developed blocks from the point of view of industrial establishments. The blocks of TABLE XXIII -^"^

Large and medium scale units' in Meerut district

BLOCKS NO. OF REGD. UNITS EMPLOYMENT

Meerut 23 13188 Jani - Rohta - Rajpura - Kharkhauda - Mawana 1 598 Hastinapur 1 1010 Parrichatgarh - Machhra - Sardhana - Saroorpur - Binoli - Daurala 2 670 Baghpat 2 1095 Baraut 1 800 Chhaprauli - Khekra - Pilana -

TABLE XXIV

Large and medium scale units in Ghaziabad district

BLOCKS NO. OF REGD. UNITS EMPLOYMENT

Garhmukteshwar - Siitibhaoli 2 1715 Hapur 1 388 Bhojpur 14 6450 Dhaulana - Moradnagar - Razapur 141 35958 Loni 9 3273 Bisrakh 23 4941 Dadri 21 2868 105

Garhmukteshwar, Dhaulana, Moradnagar in Ghaziabad district and Jani, Rohta, Rajpura, Kharkhauda,

Parrichatgarh, Machhra, chhaprauli, khekra, pilana do not have any large and medium industries.

6.2 SMALL SCALE INDUSTRIES

The role of small scale industrial sector of industrial development in particular and in overall economic development of the country in general, is beyond any dispute. The growth of this sector has been one of the most significant feature of our planned economy, The policy of government towards the development of small scale industrial sector mainly envisages the socio-economic upliftment in the country.

The development of small scale industries which by and large involves employment and income generation is one of the factors in achieving balanced regional economic growth.

For a proper assesment of the levels of development and typology of backwardness, it is useful to study not only the quantitative expansion as measured by number of units but also the qualitative aspects of development as revealed by the level of 106 technology, employment generation and investment.

Keeping in view an attempt has been made to study and analyse the temporal trends in the developmental patterns of small scale industries in Meerut and

Ghaziabad districts. The data of small scale industries on block level for Ghaziabad district is only available from 1985 to 1990, while the data pertaining to Meerut district is available from 1960-1990. Therefore, it is not possible to present a comparative picture of both the districts. The blockwise trend line for Ghaziabad district therefore, could not be drawn while for Meerut district it is calculated for determining the trends of industrial establishments, employment and investment.

6.2.1 A study of rate of increase or decrease of industrial establishments over time will show the cumulative effect of forces playing their part and will help in understanding the direction of industrial development in the study area. Keeping in view, linear growth of industrial units, production and employment have been calculated by using regression equation of Y

= mx + c^. Where Y refers to the linear growth trend 1. Harmond R. and Mc cullagh, Patrick, "Quantitative Techniques in Geocrraphy" . An introduction, clarendon Press, Oxford, 1978, pp. 99-101 107 model and x is time variable. The trend values thus obtained for industrial units, employment, production of Meerut district for the four quinquennial periods, i.e. 1970-75, 1975-1980, 1980-85 and 1985-1990 are shown in Figure 12.

The total registered industrial units of small scale industries in Meerut district increased from 236 in 1970 to 2064 in 1990 with a growht rate of 774.57 per cent. The employment increased from 3020 to 8123 persons in 1990 recorded the rate of growth 168.97 per cent. Similarly, the production of small scale units has been continuously rising from Rupees 1015.16 lakhs to 7734.12 lakhs in 1990. The trend line thus show an upward scoring of registered industrial establishments, employment and production of small scale industries.

Positive linear growth rate is calculated in terms of registered units, employment and production of small scale industries of Meerut district.

6.2.2 The concentration of small scale industries in

Ghaziabad district is given in Table-XXV and XXVI. It may be seen that prior to 1985 major concentration of industries was found in Razapur (1874) , Bhojpur (380),

Hapur (359), Loni (247), Dadri (151), Moradanagar lOS

•^ <^

in oo •-

-V, IT) o Q O o CL o o o 8 8 8 o o o o Q o o o 8 o o o U3 tn o

LU o

>- in CD I— I I/) o cr CD < ^- m ^ UJ >- CVJ Q C/f O m ^ »- t f- 5 Z O) QC 3 *• . o UJ UJ Q 5: LU o o o o o o o o o cr o o o o o o o o o o o o o o o o o o LU in CO CM

h- o o LU m Q: CO LU -J O o '^ '^^ oo cr < < UJ o '^^ >- to in

CO o

o o O o o o o o o o o O o o 00 o o o o o ID CM oo lO vl CM 109

(148), Bisrakh (83), Simbhaoli (16) and Dhaulana (17) blocks of Ghaziabad district.

TABLE XXV

Small scale industries of Ghaziabad Distt.(Before 1985)

Blocks No. of units

Loni 247

Razapur 1874

Bisrakh 83

Dadri 151

Bhojpur 380

Hapur 359

Garhmukteshwar 34

Simbhaoli 16

Moradnagar 14 8

Dhaulana 17

Total 3309

Source : District Industries centre, Ghaziabad, U.P.

Table-XXV indicates that number of registered units in Ghaziabad district increased in all the blocks of the district prior to 1985. The number of small scale units employment and production during 1985-1990 of Ghaziabad district are shown in Table-XXVI. liO

TABLE XXVI

Small scale tinlts of Ghaziabad district (1985-1990)

Blocks No. of units Employment Production (Lakh Rs.)

Loni 853 1357 1046.06

Razapur 2578 9043 21820.16

Bisrakh 670 993 1691.21

Dadri 352 505 1023.67

Bhojpur 472 1008 2713.32

Hapur 140 689 629.30

Garhmukte- 53 89 18.60 shwar

Simbhaoli 69 35 16.71

Moradnagar 84 134 312.47

Dhaulana 717 34.5 466.58

Total 5988 14198 29737.54

Source : District Industries centre, Ghaziabad, U.P.

The total registered units of small scale industries in Ghaziabad district shot up from 3309 before 1985 to 5988 in 1990 with a growth rate of 80.96 per cent.

6.2.3 Registered Units The number of small scale registered units and their rate of growth from 1970-

1990 for every block of Meerut district is given in Ill Table-XXVII. The highest growth rate (2466.66) per cent

TABLE XXVII

Small scale registered iinits in Meerut distrct (1970-1990)

Blocks No. of units No. of units Growth 1970 1990 rate (1970-1990)

Meerut 206 1449 603.39

Jani 1 1

Rohta nil nil nil

Rajpura nil 3

Kharkhauda 3 76 2433.33

Mawana 5 54 980.00

Hastinapur nil 14 0

Parrichatgarh 4 300

Machhra 1 13 1200

Sardhana 4 126 3050

Saroorpur nil 1 0

Binoli 1 2 100

Daurala nil 26 0

Baghpat 5 14 180

Baraut 6 154 2466.66

Chhaprauli nil 8 0

Khekra 3 90 2900.00

Pilana nil 29 0 112 is recorded in Baraut while the lowest is recorded in

Binoli block (100 per cent). In between this range the high percentage beside Baraut is seen in Khekra (2900.8 per cent). Kharkhauda (2433.33 per cent). It may be seen from Fig 13 that number of registered units has been constantly rising from 1970-1990. Medium positive growth rate is recorded in Mawana (980.0 per cent),

Sardhana (3050 per cent), Machhra (1200 per cent) and

Meerut (603.39 per cent) blocks. Parrichatgarh and

Baghpat blocks registered low growth in terms of number of units as Parrichatgarh recorded (300 per cent) while

Baghpat block registered (180 per cent) growth rate during this period.

The remaining six blocks namely Rajpura,

Hastinapur, Saroorpur, Daurala, Chhaprauli, Pilana did not have any registered industrial unit in 1970.

Saroorpur block registered only one industry in 1990.

Rohta block did not have any industrial establishment till 1990. In Rajpura block the first two small scale industrial units were .registered in 1975 and by 1990 the total increased to 3 units. The growth calculated for the period from 1975 to 1990 was 100 per cent. 113

O \« ri 1 I s\ 1 -

2 lA r in LU •s^ X ' ''A "•- -s < a. iC >• 2 \\^ - p-

O s «o -* o ^0 f^ O o o o o cn o •1

< - OO V •i z t/i 5 < \ CC O < < ^^^^ ^^ o z< +/« U

in - r^ CO

O 1— 1 , , • 1 ^ cn ' O o o o o •J ^ ^ i ^ ' i r- m fn — -IOD r C> . r° Ol () a: ^"X^--;---. LU - 03 ^^ a: < \ cn •s 3 CD lA to < *s < CC rO to X a. O) X < o o 1 •1 UJ c3 uu CD < H- vv / < rr I VS. 33 en 1 X. • ^ III 1 UJ 1 111 » O o < o o o o ^ ot 5: o o o ^ 2 <0 i ° u> r^ 2 o in IN* ^- r o 1 ---.,_•> "'-^*. • \ -i

lA < ~~'- • 00 ^^"•--- -g ~- \ z t/1 < I CC CO 1 • il o < a: UJ 2 ^ < -1 >-

lA

\ f \ > -i V \ o in lA in lf> •/> CTl O O oi «i n cJ ^ o <7» f- lA rt *- . o \\ \\ \ \ 'i liJ "e-i to < \ \ X \ \ (/I -i l/» X cc "i 2 < < -i >- -s

J , t- 8 o o o o o o o o o o r r* 'J O a» <^ o CO in ^ 114

Hastinapur registered industries from 1980, giving a growth rate upto 1990 of 366.66 per cent. Daurala started industrial establishment from 1975 when it registered 2 units. By 1990, all 26 units were registered in this block, the rate of growth from 1975 to 1990 was 1200 per cent. In chhaprauli the- growth rate in terms of registered industrial units was calculated for the period 1980-90 and was 700 per cent.

Pilana registered 9 units in 1985 and 29 units in 1990 giving a growth rate during the period of 222.22 per cent.

6.2.4 Employment

The number of persons empoyed in small scale registered units and their rate of growth from 1970-

1990 for each block of Meerut district is given in

Table-XXVlII.

As it is clear from the Table-XXVIII that highest rate of growth in terms of employment from 1970-1990 recorded in Baraut (1453.33 per cent) while lowest growth rate was calculated in Baghpat block (32.80 per cent) . High percentage is seen in Khekra (340 per cent), Sardhana (325.64 per cent). Medium positive growth is recorded in Meerut (131.47 per cent), Binoli llfj TABLE ZZVIII

Eiq>loyment in small scale industries in Meerut district (1970-1990)

Blocks Employment Employment Growth-rate in 1970 in 1990 (1970-1991)

Meerut 2259 5229 131.47

Jani 23 23 -

Rohta nil - -

Rajpura nil - 30 -

Kharkhauda 42 168 300

Mawana 86 138 60.46

Hastinapur nil 46 -

Parrichatgarh 22 36 63.63

Machhra 73 118 61.64

Saradhana 78 332 325.64

Saroorpur nil 44 -

Binoli 34 58 70.58

Daurala nil 208 -

Baghpat 253 336 32.80

Baraut 45 699 1453.33

Chhaprauli nil 27 -

Khekra 105 462 340

Pilana nil 169 - 116

(70.58 per cent). It may be clear from Fig.14 that number of persons employed in these units has been

constantly on a rising trend from 1970- 1990.

Parrichatgarh, Mawana and Machhra blocks registered low

growth in terms of employment in small scale units between the year 1970-1990. Parrichatgarh recorded

(63.63 per cent), Mawana (60.46 per cent) while Machhra block registered, (61.64 per cent) growth rate during

this peiod.

The remaining blocks of Meerut district did not

registered any industrial unit in 1970. Saroorpur block

registered only l unit in 1990 in which 44 people are

employed. Rohta block did not have any small scale

industry till 1990. In Rajpura block small scale units

registered in 1975 therefore, the growth in terms of

employment was calculated for the period of 1975-1990 and was 66.66 per cent. Hastinapur registered

industries from 1980 giving growth rate up to 1990 of

228.27 per cent. In Daurala, growth in terms of employment in small scale industries for the period of

1975-1990 was 462.16 per cent. In Chhaprauli, the growth rate of employment was calculated from 1980-1990 and was 800 percent. Pilana block registered industrial 117

o

in < en

Ul i/» CC I / ^ eD - «o < en liJ 1 1 I > 1 ^^^>\ •IC -,._ *^^^^ tn

O i/i in in i{» in in in in in IC; r»* r- <^ F- ^^ \ _/ • ao m < en - 03 1— in Q: 2 a. _.. -"""\ o < o •<' \ - UJ -1 •1 a. in in - r- en (/) ~^-V \ '•~^-. o *•* >v O r- tn en Q CNJ (X) »* O (^ (N ^ iC iC tC ^ i/^ cn K r^ 2 O r *^ UJ - 6 < o '""'""'""-- 'l\ 1- t>. "—1'*- in •/ \^ / 2 c^ • 1^ en \ / \^ ,-''' UJ 2: \ / o '"" ^, ^ fa- 6 4 ^ b o tn ' • 6 ' 6 b b ' o o f;; oo 3 o a> K in in i/i in in j: 5: in »J n fsi — "^ ^ o UJ r ffl < (n Q in >- 3 - «> < in o I in CO in _J o "^ It I . a: < Q- < o

\ (71 \ t \ I t - u^ < in ' 9! a. \ --'' 1 \ , - I \. ,--•' ? str --'' \ a I JV--"' in <-•* ^\ ,rf—-"" \^ o S . o < < - eo ''A a s en t . in r- -—_,

o o cn A b b "" A • A 8 g § 8 § 8 » K s ^ ^ 1.0 rsj 1^ in sj n p.* •— 118 establishment in 1985 thus their growth in terms of employment was calculated for the period 1985-1990 was

43.22 per cent.

6.2.5 Production

The production of small scale units and their rate of growth from 1970-1990 for every block of Meerut district is given in Table-XXIX.

Table shows that highest positive growth in production is recorded in Baraut (17692.20 per cent) while low growth was calculated in Kharkhauda block

(23.16 per cent). High growth in terms of production of small scale units is seen in Sardhana (2918.88 per cent), Khekra (238.17 per cent), Mawana (637.51 per cent) . It is evident from the Fig 15 that production of small scale registered units has been constantly on an upward trend. Medium growth rate is recorded in Baghpat

(166.57 per cent), Machhra (73.92 per cent), Binoli

(100 per cent) . Low growth rate is recorded in

Parrichatgarh (48.29 per cent).

The remaining blocks namely Rajpura, Hastinapur,

Saroorpur, Daurala, Chhaprauli, Pilana did not registered any industrial unit in 1970. Rohta block did ll'J

^* —— \ .-___

•— Q<. I v-]>» \ **^^* ^ O ^ o<

• \ 120 TABLE XXIX

Production of small-scale registered units (197 0-1990) in Meerut district (lakh Rs.)

Blocks Production Production Growth-rate in 1970 in 1990 (1970-1990)

Meerut 797.27 5943.61 645.49

Jani 7.80 7.80

Rohta

Rajpura 10.63

Kharkhauda 83.10 108.16 23.10

Mawana 19.59 144.48 637.51

Hastinapur 18.60

Parrichatgarh 4.70 6.97 48.29-

Machhra 6.71 25.70 73.92

Saradhana 7.55 227.92 2918.80

Saroorpur 3.50

Binoli 5.00 10.0 100

Daurala 57.25

Baghpat 21.72 57.90 166.57

Baraut 11.54 899.22 7692.20

Chhaprauli 5.40

Khekra 50.19 169.73 238.17

Pilana 37.25 121 not have any industrial establishment till 1990.

Saroorpur block registered only 1 unit in 1990 in which

the production of 3.50 Lakh Rs. in 1990. In Rajpura block production of small scale units and their growth was calculated from the period of 1975 to 1990 was

27.76 per cent. Hastinapur registered industries from

1980 giving a growth rate up to 1990 of 90.96 per cent.

In Daurala growth in terms of production was calculated during the period 1975-1990 was 823.38 per cent. In

chhaprauli growth was calculated for the period 1980-90 was 145.45 per cent. Pilana registered industries in

1985 therefore the rate of growth in terms of production of small scale units in this block was

208.36 per cent during the period from 1985-1990.

6.3 Polluting Industries

In the age of nuclear weapons, the human race is facing menace by another equally homicidal missile describe as "Environmental pollution". Man's only home planet, earth is under homicidal threat through pollution of environment. The source of life is oxygen and this human planet of ours will perish if by pollution we destroy that fountain. In the interest of 122 the present and future generation, the necessary step required to be taken as to make scientific and rational use of the land, its mineral and water resources, plants and animal kingdom to preserve the purity of air, water, ensure reproduction of natural wealth and improve quality of environment.

Every industry create pollution in the form of smoke, effluents, noise. The nature and quantity of wastes differ from industry to industry depending on the nature of raw materials and processes used and products manufactured. Water discharged from most of the industries are invariably contaminated with small amounts of all materials and chemical used in the plant. The volume of waste water discharged also varies from industry to industry. Despite the explicit policies of industrial dispersal of the 1960 and 1970s, the concentration of industries in and around major urban centres has continued. The large industries that can internalise the entire production process have moved away from urban centres to take advantage of the various subsidies and concessions. However, the small scale sector and^ the unregistered industries have preferred urban areas. Such industries in urban areas 123 have been causing severe water and air pollution. The over all impact of existence of industries on urban

environments is an increase in smoke, noise, heat, gas,

fumes which not only affects human health but also properties. Industries also cause land pollution attributable to dumping of solid wastes in open areas, which get leached into the soil and pollute the soil as well as the ground water.

The central board (for prevention and control of pollution) indentified major polluting industries of the study region. These industries mainly of chemical,

sugar, tannery, textiles, dyes units, fertilizers and pharmacuticals as given in Table-XXX and XXXI. These

industries not only polluting the environment but also creating high-risk condition to the people living in the nearby areas (Fig 16).

The main site of discharge toxic effluents are river Hindon which passes through the city and river

Yamuna situated on the western part of the city.

Concentration of pollutants in waste water varies from one type of industry to another industries which discharged their effluents into river Hindon are 124

"m e- .•fo-

"o 0° _CD r-

en »— 0

CO */) Q UJ 0: :< Q ^- < to CD 3 ^ < 0 M 2 < X CD Q Z F < z> i -J r~ 1— 0 3 a. UJ UJ

JC 125

4J 4J l*-l c C 01 O r-l OJ OJ c 01 01 Ol 01 0 e e -rH c c c c c -H -rH -H -H 4J 0) 0) U 0 ai r-( r-l r-l rH -H c 4J 0c IcD (0 u u u u -H u >->.>.>. 01 u i-l V4 u u u u u (U 0) OJ O c (0 (0 a o 0) ^ ^ ^ Q) (U CU (U CU cu CU lu 1 -H .-1 iH iJ r-l I-l 1-H rH 4-) 4J 4J 4J 4J 4J 4-1 1 4J u r-l 4-1 (D 10 0) (0 (0 (D ID cu cu 0) tu (U (U (U CU 1 U (0 D •H •H l-< -rH •H -H -rH f-{ I-l r-l rH rH r-K rA T-\ 1 •H D r-l 4J 4-1 a 4J 4-) 4J 4-) a a & a a a a Q< ' M 4J r—1 M u E t4 VH ^ ^1 E E E E E E E E 1 u o ID (0 o (D ID (0 ID o o o 0 0 o O O o o o 1 •i-> < CL CU a u a Ol Ol CU 2 U O 2 a u u o a u u 1 CQ

•H tn 1 Q - >. ^ >< . >1 "--v 1 ID (0 cn ID >, >i ID tn 1 X 0 TD TJ C T5 (D >i >i >. >, ID 73 cu 1 >> ^v^ ^^ 0 -^73 ID (D 73 1 4J cn cn 4J cn ~^ "O T) "O Ol •H 1 n -H -a -^ 0) c c C cn •^-^^ ^^ cn X U 1 U >. o 0 o 0 C tn tn cn cn C >1 •H 1 •rl (0 ID >. 4J 4J rH 4J O c c c C 0 >1 o ID 4-1 1 * 0 1 3 1—1 f—i CD C & O O O O 0 (X iH u -H 1 -D o O w •rH CQ CQ OQ 00 m u 3 3 4J 1 (7) O £ x: i-l 4J 4J 4-1 3 X X ID 1 U O 0 u 0) C l*H rH rH rH rH r-l MH 0 a a E 1 -cH 0. u u c a -H (D rH rH rH rH f-l (0 rH rH rH U ' JJ r-l rH •H ID VH VH -H •H -H -H •rl iH o 3 3 0 1 < < N a- O- U 2 2 2 2 2 U u c;} W Cb 1 , H T3 M (D 4J 1 0 D (D 0 3 ' 04 >- a in rH VH 4J i c 0) (D 10 0) 3 1 dJ •H •H c 10 CU U 1 X! x; 4J C 2 Q) VH ID iH D •-> 4J (0 CU 1 -H a ID • 1 D -H ~ • iH CD D ID 0) • > U tn 4J 4J 1 • T) ID 73 2 4J CU > 3 1 eanj i-i •H at3 4-1 o - O IH > ID 4J rH 0 73 CI* iH 1 -f-t ? 01 4J ID 4J J CO rH )H CU - a. U 3 r-\ (0 iH -H 0) 1 VJ M r—l VJ a •:! rH Q. Qi rH •M -H iH 10 U Ol u tn CU 1 4-1 i—l (U ^H u» •H (0 4J r-l U •M E (U o -H <; -rH rH 2 ' w ID •H M-l ID iH 0) E iH a. D -H (U 3 (0 d) -H E i-> ID 1 D n r-H 4J n u , ro cfl a ID ID CLi ID 2 VH (U o cu u u (U 0) 10 C (U . ID ID OJ S >i 3 0) OJ •0 rH M X X 1 i -H £ rH . 73 4J U 5."="; 4J •H U •H D s: s: M 3 VH (D i>i iH D i]l rH ID Q 3 -H • ID O iH 1 • - 1 4J K 4-1 4J •P cn SH Ol ^ OlT) -H M •r-l E CD (0 ^ 73 O U .P tn iH u tu 1 M-< ta cn H C V4 cn a; H cn C ^H rH cu >,:-l > .x >. (0 O i i 0 O J^ 0 a 0) 0) (U X ID X 1 Q X D U fc S 2 P. 2 WWitJSSi'iZ^ >5 U T)Q • 0) e , (0 > • • » 1 rH z H T—1 CN T-\ r-l CN ro 'S' \n o r~ 00 tT\ H cs ro > t-1 CN ro 1 126

c o 01 -H 4J c •H u r-t U 4-) en u c 0) 0) o dj 4-) u i-H 0) u 0) ID 1-H u -H a (U tt-u e T! e V4 0 0 o C 0 0 (0 0 0 u s; !Z D 2 u a< a 2

>. >, >. >. >i >, m (0 (0 (0 Hi ID n -a T3 n T3 "D ~--»^^ en Di ^-0»1 ~^01 ~O^l "O^l c c c c c c >, -H -rH •H •rH •H -H' (0 >i >, x: x: JC x: x; x: T) ID ID 01 CO- w tn in K "^ •D •D 3 P 3 3 3 3 01 ~^ -^ v< ^ 1-1 S^ W U C • u u u u U U -H 01 Ol (L)

3 tD x: OJ ID 4J o (t3 ID •H s m r—1 rH a (D - ID - rH i-i tn e tn i-l o a r-i (0 (U 3 u (0 - r-4 * a •H a 4-1 Q C c •H c U ID c O 0 E 0 ^ J-l 4j 0 - -r^ -H •H r-l (0 ID ij u M 4-1 4-1 >H 4J r-1 C i-( ID y: ca (0 (C ID •H (0 0 a c U SH u 01 ^ e 3 X3 o O 0 0 3 0 ID ID * -H 3 a a W Q. •H s: >—< 4-1 ^1 tj U 4J c TJ 3 U O o (U O 3 OJ - .—. iJ rH to u o U 0) tn 03 J rH CJ) -r>i 0>^) x: j^ U 0 D *-i i-i 4J Wi (U U V4 •i-i • a. W (C n3 to ID S 0 m e iJ 01 Oi ^ 01 •H S H fH (t3 3 3 OJ 3 « u « x: 04 ID rH C/l C/3 (0 a CO i-l ID VJ u u 1-4 (D > n 0 3 j<: ID •H 1 ID 4-) i-i 0 4J 0) c 0 0) ax; oi+J 0 E c 3 4J •H 4J to a u c ID 3 3 V U 0) (0 (D u (0 H ID •t-f C/3 M 9 c ID o Q 4J 4-1 4J 4J 4-> T3 U t—1 x: C/1 U M •H (tj ID W "D ID ID « 4-1 Cb h • 3 4-1 a a 3 ^ C 3 1 * tn • >-i 0 x: £ • •H (D ID g tn w tn 0) en a. 0) a. j^ Dl Dicu x; e 3 Id tn (U 4J 3 (U • 0) to (D ID • 0 ID ID i3 0) G ID d) W S D Z D W CQ u mnsccsoisss u H 3 H • . • H • 0 > rH CM ro ^ in 1X1 t^ > rM IN (0 127 textiles, pulp and paper and board, distillery, chemical, metallurgical and processing work.

There are three big distilleries in Ghaziabad district discharging huge amount of waste water into waterbodies. These are Simbhaoli industries, Modi distillery, Modinagar and Mohan Meakins. Mohan Meakins discharges the most toxic effluents causing severe damages to the soil quality of the adjacent land on which it is discharged. On the other side, in Meerut district, Daurala sugar works and central distillery also contributes their role in spreading water pollution to the adjacent region. Only partial arrengement have been made in the factory premises for controlling pollution problem therefore, they advised to installed proper treatment plant inside the industry and then waste water should be allowed for disposal.

There are six fertilizer industries in both the districts that also share its role in increasing water pollution of this region. Major concentration of fertilizer industries are situated at Ghaziabad. pulp and paper industries are the main water polluting industries of the study region. In few industries partial arrangement for controlling pollution have been 12.S

JJ JJ 4J JJ 1 It-I 1 U 4J J-l c JJ JJ JJ JJ JJ 1 ' 0 i—i ' C C C c01 dcl QcJ 01 C C C C C 1 o d, O 0) e e E E 03 03 0) 0) 03 1 > c (-1 E e e 0) 0) 01 03 E E 6 E E 1 < 0 J-J 1 01 QJ 0) Dl en CD C71 03 03 03 03 03 1 1 -H c • 01 CTi tJi JJ C C C c UjJJJJJJJDlDIJJDlDl-UJJjJJJJJjJDlJJJJ 1 1 4J o 1 C C C C ro (D a3n30303 i I CO 1 >-i »-< ^j E V^ M >^ u EEegEMME^H^iEEeeEElHEe 1 1 O c 1 V^ Is 1-4 Q) (0 (0 (0 Ha3a3a3a303a3VHa303 i 1 a o 1 (0 (D <0 OlDlDiDlDiiO 10 DiiO 10 DlOiDlCnOlOi'O OlD) i -H cCn 0) 0) 0) 03 CCCCC C CCCCCC CCi 1 r-4 JJ 1 r-4 r-H t—t ro JJ JJ JJ iJ (OlOIOlOlOrHrHIOrHrHlOlOlOIOIOlOrHIOlO 1 1 m 3 1 (C (0 (0 U 0) Oi Q) 0) l-tVj^HiHMIOIOlHlOrOSHlHiHtHlHiHlO^iH 1 1 3 t-i 1 -H -H -H i-l rH I-I I-H rH ^l^l^^^^^^.H-H^J•H•H^H^HiHW^H^H-HMlH i 1 iJ i-i 1 JJ JJ JJ

to (0 (0 nj -^ T3 T) Xi 03 c 03 n CO o C C C H >i i >, O O O (0 >i 1 (0 H H H u XI 10 >i >. 1 -H '^ X) rO ID 1 u \ u u u w to -•-^ >, X! Xi >, 1 m -H -H -H JJ C 03 10 ~-- >i'\ ID >i >i 1 -H C i^ S-i M 03 OCXf>i>i 03ID03XI >,>.iD(Oi 0 JJ -u JJ EHO\iOiO>^>,>,>,CX!q--->,>,iDiDX3T3 ' E-1 OJ OJ Q)s EH03X!X)IDlOIOIOO~^Oa3IDlDXlXl~-^^- ' 4J s s s o U C^^^^X)X)X)T3EHtnEHCX)X3"^"---a3 03 i n u o •H U 0 03 03\.\^-\ C 0^"\ 03 03 C C 1 •H •H (N PI C\ rH >H-rHEHCCm«)aito •OUHwinCCOOi Q >1 u jJiH OOCCCCSEH-H •CCOOEHHI t-> JJ Q) Q) 0) 03 OI-P-EHHOOGO -VISOOEHH 1 •0 -H 1' >cc >in. fD> . 0) JJ -U 4J JJ 2032 EHHEHHO2-W HEH ..I Id u 1 "O T3 X) S <0 (0 (0 (0 2 • • o 03 o • • 2 S 1 Xi (C 1 ~~^^^^, x: £ x: £ in 022----rHin2rH-.2S ' <0 a • o a a Q, a •oo 2222 • 2S oini •H (0 1 1—1 T-H rH CN 1—1 r-H rH rH rHrHOItNVD iHlNiniH mrOVO'l u M St: ici P 3 3 3 (NininiNOJrHrHOICNCO rHI N m W3 CO COC O --iH^I^I a a VHVH>H 1 Id c ITi VC O 1-1 X!X!Q3O)03T3XIXIX!lDXIX)lOX)Xlfl30)03'd i H ji 0 r-t r-i r^ 0} e E e SHMaaa5H^i>HMa>HkawMaaaiH i •H N 3 D D 3e lOlDlOlDlOlDIOlDiD lOlD IDIOIOIDIDIOI o JJ r—1 r-i ,-H •H -r-l -H -H -H GoaaaooGODiooDiooaaao i 03 -( tji Dl in cn rHiHlDlOIOrHrHrHrH-HrHrHCJrHrH x; 1 n ID X3 O 1 XI 10 1 10 X) X) - 1 -rl (D ID 10 10 1 H N -H (0 X) 03 1 ID N X! ID iH 1 XJ .d 10 10 XI < 1 (D o x: -H -rH 1 X3 XI o N x: • 1 -H (0 10 •• ID 10 X3 1 •H X3 ^1 - x: CO c 1 03 N ID ID ^M O M 1 i-i J2 m -H tn 10 * ' (0 x: N ID D1 - ID - X! 1 TD O X3 IDCIO <-i 03rH X3X)X)'OlDX! i 0 T; to N (D X) ID X:-H2 rH iHrH lOIDIOlDXJID > (U X3 - Tl (0 ,Q OXIX) -H X)<:-H X1.QX1X)I0X1 1 x: ::; x: XI 10 OlO E ID EX5I0I0I0I0.OID i •H T) XI (0 •rl - 2 in XI rH ID -H -H -H X! -H XI 1 — N N JJ 10 •H X) NXllH G T3 IDI0X3X1NNN-Hx:-H i N .-3 - (t3 iJ -H N (0 IDlDlO»2 iH -H-HiHIOlDlOIOX;iDx: 1 fC -C H x: N fO X3 x:x3DirH 10 NVJIO-HX:X:X:IDCOIDT3I x: c m U • (D x: ID oioiOrH- 0 iDiJONCjocnco coioi JJ x: o H -HC-rHrH DQ x;D3oaro - xii - IT3 - > o N -N-rlEr-IXJ 03 X;-'--rH >lOl tn - M 2 • a * (0 031013 -HiDTaTD XJXlOrHXJXlrHrH -XJi (L cr, ^ n -n 03 x: rHX;OX)E.QClO -CC rHIOIOrH-HX)-H 1 -H C cr. C U rH • (0 u o rH02^J lDlOXla3M(0 --HX1X3-HE4J.C 1 (- •'-' cz ^ J in "O XI 01 •H (0X3-H iDiH -HglDlOE taiOi o •- 2 x: U JJ It) N » E>-OVHNH-niU-iHC .QX3 X! CO' i-l - o • -H J -H •H H •030QlOlOfl3NC •03OiH-H-HX!iH • 1 u m •- s JJ e N rH c tixirH G.caio-HXJaf^o),cx:iHiojj -i fC Z3 "^ > (0 • (d •H 0 03jjrHX)(ntDiox:iowio aioiDioo>rH i a x: -u x: 4J J ttfj-HC &,ajj|ja< -lococoocQCLirHi ^- = s: • u > o in lOEiO'^a- c r-t cu 03 -rii K 1- T3 tn a* 0) a^^ <-< -r-i ~ O • •'-< r-\ .. XlrHEl JJ - U u u 1*H 03« . 0)lHiHVHrH>HrHCj4J4J-H-HrHrHX)CrH 1 •r- — NJ 0) 0) 0) 05 r-i taa03fl303-HIOrH >OE-nrHrHClO-H^ 1 C — M N N Ti 0) r-< (0 loaaaExi-H-oaN IO-H-HIO EO3I ^ Cot/; -rH -H -H -H (0 u aaioioio -HEC "-oxirHEE in ai a .T; — c M rH 03 VJ U rl HrH aaaMOQ 1003 iHiD 1H03WI0I di e x: r- -r-i n •r-( -H 0) JJ -H E »3'^ a3iVH X3CiDDQX3VHfl3aQ3ai J: -H £ •- ^ M JJ JJ C 03 E 03 0,04 iHJJJJail3H Dl 3 03 lO aioioioioji^aiHiojJCQO)iDaioaiD-H i « -1 K 0) N 0) 0) (0 73 x: x: oiiHrHDiiHiHaiCioiDOio ojoioa aj->i l*- I-I cn -1 s -H !« ijj s: c U u 033IOIOIO iDaooQoJrHiHcna s: lOi 0 I-I Q H M H i»-Ha42;x;x:.cco CQ IOX; rHcoecoi •H • C -rH >, E >i (0 4J jJ DQCQD3 rH lH'JJCOO3lOID033 ' OJ 4J Ul -^ (0 -U (0 03 (0 iH C 0«CO-H fl3-H 10 -030303 IDjJCn-(^iExJ>>c^i apu a 03 03 >,rH a c c cn c < rc •H 0- 0 O 0) •rH (T3 -H 03 x: aOlDOIOlOIOXIO •lDQ3x:iOiJ303lOlDlO 1 Z Q 2 S S fc > a, > CO 2 -0 S[i4U222OC0OtDa42C0f3

c o •H 4J u 3 4-1 CO c o 0) (U 1 1 i-H i-l i-l rH u 4J U 1 1 nj nj (0 (0 0) (U 1 1 -H -H -H -rH 1-1 rH rH 1 1 U U iJ 4J QJ & a 1 1 ^J U V^ U XI E E 1 1 o o o o (0 ro o o

x; 4-> c o E

CO c x: X >,>,>, O 4J X 0 X X 4J x; 1 to m- (0 E c £ >. >i 4J >, H 4-) 4J C 4-1 tn 1 1 TD TJ "O ~^ O 4J (0 (0 >^ C (0 >, • c c o c >, (U 1 1 "-^"v,~>^ m E c >,T3 -a (0 >, >. 0 T3 (0 2 0 o E O 10 CO XJ 1 1 w tn m c "^ o ra ^^^^T! (0 ID E •^X) "\ E E^ E X5 0) -H 1 1 C C C O CD E T3 DO CO ^-v TD 73 ^ CO "^ O -v. --X CO -^ "^ XI >1 U 1 ' 0 O O E-i C "^ ^\ c C tn "^ ~^ CO C to •<}< CO CO C CO CO X -H 10 -H 1 1 E- H H • 0 tn m O 0 C to cn C 0 C CN c c 0 C c 4-) u XI 4J 1 • • 2 H C c H H O C C 0 E-i 0 o OHO o >1 c -H ''^v to 1 ' >, • S S • O o • • H o OH • E-i ^1 E-i H • EH EH ID o 4J CO 0) 1 1 (C S in S £-" E-< 2 S • H E- • 2 • tu 2 • X) E CO 4-1 a 1 ' "O in in • S • 2 2 tt 2 2 2 2 ^^ '-v. 0) CO -H ' ^-^ >H • • tN o 5: S o o 2 2 in ID o Di CD a.i^ c MH 1 1 en rH rH i-H rH t-l rH O o • o tt o o rH in 00 t.£i c c 3 0 >, 1 ' C - tN (N I-l CNi f\ m CN rH ro ro CN) 0 MH ID ID 1 1 0 T3 - > -. - "O in 4-1 XI "^ IH o H 0 4J 0 C XI 1 ' 8- i-i'D'O'O'O'OX! i-l 0) T3 "D •C T) T) T3 iw XI T3 iH XI -l u (0 a k i^ M in W k ID i-l iH ID U a in 2 c 4J 0 •H CD 1 i U 0 (0 (0 (0 <0 (0 (D O (0 nj <0 10 ID ID ID i-l ID 10 O ID (0 0 •H - 4J C 1 ' -H QQ O 0 O O 0 0 CD a o O 0 0 O 0 U o 0 m o a CO "^ -iH a 0 ID 0 1 1 i-i OQ CO CQ CQ CQ CO CQ CQ 03 CQ OQ CQ OQ m CQ M CM 4-1 JH rH rH EH 1 1 XJ U S-l 4J 10 X i-> 3 10 10 2 ' 1 » ID u 1 X ro T! (0 X XI (0 (0 c Ct X X Q) 4J x: 10 Ch CO rH X CO r-t ^ 1 > tc M m X o XI XJ X) -H X E c J 1 ID 4J 4J E ID lU 0 1 C/:-H(0J3(DCOlO X XI en • ID xi 1-1 a< XI E X -H X 0 ft! I-l« -H J CO 1 - O • <0 X) XI I-l ID -H XI H^ H^) X 4J -rt £ O J 2 >. (0 4-1 •H 1-1 C iJ 3 Q E 1-H 10 XI N U XI c 4-1 1 1 (U T3 X (0 C (0 > N •H 10 ij DQ r-{ -iH 10 ID U 1 u • • u * ID w 'M CO CO - - -H <0 CO c Oi 10 E ^ >XI •H N 4-) U ID X LS X DI 3 1 •r-i (0 U3 -H t-H > Di (0 en 3 • -r-< W 10 O IH ID 0 XI 1 X E > > o 4J • a: 0 - c --^ (0 . iH 1 en - r-t O -H t C -H O XI o 3 N > XI XJ E r-l r-1 J E I-l •K <0 t-i r-i U 1-H* . 4J ->O . (0 10 a 1 - G. 0 E oa u D ID • ^ TJ '-1 -^ -H .—( - -H n o en CO ID >.r- H r-{ 0) r-^ n X X ^ c -H E - -a I-l > rH I-l E (0 CQ X ac 1 1 (0 (0 -i t-i (0 C TO a , C 0) (U CQ (D •H (0 o a CQ ID ^ 10 XI 4J 4-) ID c (U 10 •H 0 0 OJ ID X iH 1 ' (0 (0 iM 0) r-l *-l •o -r-l (0 E « CO la 0) M i-l a c (0 ID • XI x: & 2 CO K a: PI 2 2 0 U 1 1 •!—1 > 3 13 4J (0 (0 >^ 10 cnx 0) X TD ID • iJ 0) -H 3 10 a Di CO H CO ' c -H a oi-H E E (0 1-1 C 10 4J CO (D i-l > C ^4 rH a •n 1-H •H 10 CO x: -H ' foxiofoE'oax (0 (0 ^1 •H 0) 0 ID • ID X fO ID ID 3 iH iH 0) ID iH > • • • • ' 1 w M I ^^ < ^ t*: CO D3 O PQ CO Q a: CL a: CO E-. t«; X Oi CQ H a 2 CO iii H rH CN > rH CM ro 1 130

0 0) 0) 0) (U 0) (D 0) 0) 0) 4J 4J 1-1 4J 4J i-< u rH rH U iH r-l 4J 4-1 4J 4J a 4J 4J ftiJ ^ 0< CX O4 OJ B e u e £ • * . >J e U ^^ e u ^ 6 e e e • • o 0

c 0 E ~^ 01 £ C 4-1 0 c E-i >i >i 0 >. > >i SZ • ID 10 E <0 (0 >i , >. C * 0 "v^ ^, 03 CO ^^-^TJ ""^ ID (0 0 01 rH 01 01 Dl c to 0] ^ 01 T3 n 0 >, E 0) C c 3 0 c c w c "-V ^, 0 ID *\ c * 0 0 SH H 0 0 c 0 01 01 in T) x; • •H 01 b< EH Q x: H H 0 H C c rH ~-- 4-1 iH u 0) • • 4J S . . h, . 0 0 en c t«; •H x; C 2 2 •H C S 2 • S E-i H • C 0 T3 4J -H 01 C 0 0 s . Q 0 E 0 01 c U rH rH r-\ (0 E 0 in 0 in X S • £- — Lfl E 0 •rH 3 01 03 CO c -^ Lf) CN 0 (N 01 a • E T3 * - 01 4J 4J AJ D x: 03 iH iH r-l Tji TH 0 0 . 0 r-\ rH U"\ 01 r-t rH tt 01 01 01 4.) C in ^ 0 0 t«: 0 -H 03 E 0 0 ID rH f-\. rH ^a c 0 -H -H -H -H -H . LD E x: C E E U XJ X3 X3 0 H 4J 4-1 4J 4J 4J •H .« E-I no 0 ID 4J 0 u (0 (D ~^ (0 (D (0 U E (D <0 (0 IT! ID ID u t- 4J ID EH •H 4J 4J 01 4J iJ 4J •rl ~^ • a a a a a a 0) » - 0 a T3 01 0) 4J^^^^"^-'OrH 2 w en en 0] 03 01 x: u u a u 0 • 01 u tj (u 0. a D. 01 « (0 leJ 10 ID to ID 4J (0 ID D ID 01 2 > (D ro rH 3 3 3 F> 0 c c c c c c ID Ol CD iH U E u SH V4 XI ^1 ^ SH SH 0 rH (0 ID (0 ID ID (D tt) 3 3 >. ID 0 0 g ID ffl (0 >i>,>i3on > > > > > > •-q o) w w a X rH < cu aiE-il/lC/ll/lieCrorH

T3 ID to N •a ID "D "C (0 —1 (D ID (D 0 XI 4J N XI XI ID 3 CD ID ID 4J N - XI SH - x: -H -r-l -H « ID ••H T3 -H •a 01 T3 0 N esi >-i n • X: rH 4J x: (0 01 (0 ID ID e ID T3 0 0 •J » ID XI 2 £1 -x: x: < XI 4-1 ID • c/3 ID IT) -a 0 0 ID hJ -x: m •o n •a -H - £1 ID -H in n r-\ 4J ID Tl - (D N 03 -H 0 - -TJ N • (D eyj •rl 4J XI (0 4J -H 0 SH M • oi 0 a 0 Cu c 4J > •H XI J N 0 f-' ID Q: •rl - D a x: -H (0 - 4J ^ • c ^ U T> tn eu ID x: • x: 01 01 (0 C 0 •" -H E-i u ID 01 10 0 (1) - 0 0 U a 4J •H E XI -H XJ * 04 - u - - 01 -H -H •rl (0 0 TD "O ID OJ n SH ID •H 01 •r( u U3 rH 4J SH 4-1 03 r:i u j_) % * -f^ ID U i-H H x; N ID N 0 T3 rH (0 3 0 3 rH n a J -n m j_i XI a X) 01 . XJ -H 01 x: M X3 SH 01 S N C r-l T3 c ID c x: "V 4J x: TD -H •p U T3 4J T3 ID T3 x; T3 U (0 <0 ID £ -^ ro -r( 0 (0 M C r-l ID U 0 01 U 0 r-H 3 ID (D c ID J c u (0 x: J x: u x: 0 J 2 0 0 > XI 01 XI H XI (0 a O. T) CD 0 (D c > 0 « IW & « U (D u ID C ID ID -H (0 >, E r-f V4 M • •H 0 4J U » •H It • x: « • XI •rH X) T) SH c •H -H (0 ID ID ID ID - en N AJ 'H (D -H ID a en M 01 01 ^ 0) -rl 4-1 •rl U 3 •H N > "O U 01 C T3 Tl H en (0 Q H S D 2 M J3 2 w u t/i m H Ol aao20DOCL,3:a: H H , , H • . . . H . H 0 rH > ^ oi rn •rf in U3 > r-l > rH CN H rH es rn 1" in «3 e~- 00 CTi rH rH 131 made besides these few industries are functioning without installing treatment plant in their promises.

Therefore, with the increasing number of pulp and paper, textiles, pesticides, Oil refinery, tannery.

Sugar, pharmaceuticals and other industries causing serious environmental threat to the study region. In the study region textile mills and few small units of the area consume chemicals for dyeing process which causes contamination of alkalies, heavy metals, oil and greese, solids (dissolved and suspended) and significant amount of BOD. Therefore, increasing discharge of effluent containing toxic pollutants will cause pollution of river Hindon, Kali and yamuna water.

Similarly, pulp and paper industry is one of the most disastrous industry of the study region requires immediate pollution control measures to be adopted.

Regarding air pollution of the study region, every factory in their premises provided boiler facilities and they mainly consume coal. Air polluting industries of the study region includes distilleries pulp and paper, sugar works, chemical units, fertilizers, textiles, cement industries and many other small scale 132 units functioning in the study region. The brick-klins also polluting air of the surrounding region. Nearly

450 brik klins are functioning at Meerut and Ghaziabad districts to fulfill the need of development of urban

sectors and other constructional activities of the study area. PART III POLLUTION: NATURE AND SPREAD CHAPTER VII 22 M

ENVIROMMEMTAL POLLUTION ; GENERAL ASSESMENT

7.0 India, being a developing country is striving at its best for rapid development of its industry, agriculture, science, technology, means of transport and communication. The problem of environmental pollution is inevitably present in every human survival enterprise and ultimately poses a threat to human survival, if not controlled in time, human survival naturally outweighs, the craze for development progress or prosperity. The entire law relating to prevention and control of environmental pollution is a result of anxiety and preference to human survival over development, progress or prosperity.

Natural system of check and balance and maintaining equillibrium has been disturbed by the human efforts in experimenting and adopting science and technology. During vedic era, Aryans were the worshipper of nature and believed in purity both in social life and ecology. They were admirer of the natural resources, gradually population exploitation put an increasing pressure on natural resources which were ruthlessly explorated and exploited. Beauties of 134 villages vanished and we witness now the smoke, noise, gas leackage and radiation pollution and many other types of pollution which have disturbed the whole environment. Industrial revolution, though for the betterment and progress of society gave birth to so many socio-economic evils like air, water, noise garbage and industrial wastes. The whole world is worried about the ecological imbalences and environmental pollution because it badly effects the health and physique of human instincts.

Any developing country can prosper only with industrialisation with the result most of our cities and towns have industries. Though, these industries have helped to solve the unemployment problem created by rapid growth of population. These industries have become the sources of air, water and land degradation.

The environment is polluted to such an extent that the people suffer from various diseases. Thus, the effect of industries on the environment is quiet alarming. The major types and sources of pollution are given in

Table XXXII. TABLE XXXII 135

TYPES AND SOURCES OF ENVIRONMENTAL POLLUTION

Pollution typ«« Pollution involvad Sources of pollution

Air Pollution Oxides of sulphur (Soj.Soj) Combustion of coal. Petrol t Oxides of nitrogen, carbonmonoxide, Diesal, Industrial processes, Hydrocarbons, Aminonia, Lead, solid waste disposal, sewage Aldehydes, Asbestos t Beryllium. disposal etc.

Water Pollution Odour, dissolved and suspended solids. Sewage disposal, urban runoff, Ammonia and urea, Nitrate and toxic effluents from Nitrits, chlorides, flourides, industries, runoff over carbonates, oil & grease, insecticide cultivated lands & nuclear & pesticides. Tannin, coliform, MPM power plants. (bacterial count) sulphates and sulphides. Heavy metals eg. lead, arsenic, mercury. Manganese, Radio­ active substances etc.

Land Pollution Human & animan excreta, viruses & Improper human activities,

bacteria, garbage and vectors present disposal of untreated

in pesticides & fertilizer residue, industrial wastes, uses of

Alkalinity, florides. Radio active pesticides & fertilizers,

sub St ance s.

Noise Pollution High level of noise above tolerence Air craft automobiles, trains, level industrial processing and advertising media.

Source : Singh, D.N. & Singh., "An introduction to our earth and environment, Environment and development study centre (EDSC) VARANASI, 1988.

7.0.1 Air Pollution

Realization of harmful consequences of air pollution is a relatively recent phenomena, but in 136 India, the magnitude of the problem has not been fully

assessed in spite of the man-made greatest Bhopal

disaster of 1984, when more than 2000 people died.

Still, pollution from industries appears unnoticed. One

explanation for this is the restricted spread of

industries and the other could be the absence or

ineffective functioning of air monitoring stations in

major cities and towns. The air monitoring stations set

up by the National Environmental Engineering Research

Institute (NEERI) in Bombay, Calcutta, Jaipur,

Ahmadabad and Nagpur are unable to formulate realistic

standards for permissible levels of air pollutants and

have lack of sophisticated monitoring and tracking

instruments.

Air, itself is a mixture of gases, water, vapour

and dust particles of which carbondioxide

sulphurdioxide, nitrogen oxide, carbonmonoxide, perticulate matter and water vapour play an important role in biological processes and the temperature changes of the atmosphere.

The air may be polluted by the presence of one or more contaminents such as dust, fumes, gases, mist, odour, smoke and vapour in quantities of 137

characteristics and of duration such as to be injurious

to human, plant or animal life and to property or which

unreasonably interferes with the comfortable enjoyment

of life and property.

The major air pollutant in the atmosphere is

sulphurdioxide (Table-XXXIII) originating as a result

of industrial operations, oil refinning, domestic use

of fuels,4 thermal power plants, when mixed with air it

causes damages to property as a result of corrosion,

destruction of sensitive crops, irritation of throat

and eyes, respiratory diseases and suffocation on men.

Another air pollutant, hydrogen sulphide,

originates from the petroleum industry, viscos rayon

plants, sewage treatment, tanning industry, dye manufacturing and oil refining and results in corrosion

and decolorisation of materials. Its effect on humans

are seen in the form of irritation of respiratory passages, danger of respiratory paralysis and asphyxiatation.

Nitrogen oxides generated from motor vehicle and acid manufacturing have in side effect on man as oedema of lungs, bronchitis and irritation. Hydrogen fluoride 138

e r-l 1-1 0 u 0 <0 C rH C -l 0 0) e U (U -H 4-1 4J 0) r-l 0 (0 TO TO 0) >. iJ 3 r-l x: M x: o TO -O (0 H a; 0) C — 4J u ^ (20 .cH u e 2 u ^a 0 i-H x: (1) >•< - o (U 6 TO a r—1 (U (0 3 c M-l 0 u •rl ~ CO 4J 1) TO Oi M-l u •" (0 -i Dl O ^ a , ^& 2 ••H 01 TO ,1 03 4J 0 * 3 (U JJ U 1 e 0 !^'o TO TO 4-1 1 V u rH QJ 1 (0 3 M > 3 TO U • 4-1 (0 0 rH o •H O > •d ^1 i^ U r-l £ (0 U 1 TO QJ •H 1 x: 0 4J TO (0 3 U u 3 £ >. 03 3 M-l U O u •H ?, TO e 1 O tt *-i (1) (0 3 -H rH 0) e <" Q) <0 1 40J Oi rH 4J B £ C £ a 3 5 "o QJ VH CO a 3 CD O X (0 0) X 0 x: -H QJ 0) cn 3 T) 0) S > QJ a S.5 u e U Ti 4-1 H u C x; c H u •u M 01 flj H (0 > ^1 3 "O >i e P en O C X3 c 0 01 o 0 X CO -C 0) C ^1 3 •a • C -H QJ > Xi 0 4J c M-l O ^ •H 0) c a 0 u U , 1 w •" v a -H X a C M-t TO c n -H X3 o u O 0 i 01 0 < . C 0^ "" -H U ' 0 « - en 4J OI 0iH 0i-1l rH C U . z (0 4-1 rH QJ : S «2 SH 0 t en •H « U (0 di • 0) O O (U -H C TO MH 10 • S TO -a a -H QJ C rH > 1 O S •H ._ TO T3 0 (U TO (0 (0 1 U •H -H O5^' "U «0)T 3C QJ QJ c u TO rH It U >1 Ti 1 00 X 0 1 00 1 M"

"o 1 TO TO u 1 4J 01 1 C 1 QJ •H TO in 1 B X 0) 0) 1 3 _0 4J 1 U •H 4J 1 O X 10 1 T5 o e OJ i >i T3 01 1 Vi !

Solid particles as dust released from the mines and grazing operations, pottery and ceramic factories and power stations lead to side effects on man by increasing respiratory diseases like silicosis, asbestosis and poisoning from metallic dusts. These also lead to corrosion of property and materials.

Hydrocarbons released into the atmosphere as a result of organic and chemical industry and automobile exhaust causes cancer on man. Oxidants as a harmful air pollutants originate due to photo-chemical process from the organic material irradiated in the presence of nitrogen oxides by silent electric discharge and by the ultravoilet radiation and have its impact on lungs, irritation on man, destruction of vegetation and smog 140 formation though not common in tropical countries .

The problem of air pollution today is a national and

international problem. Nowadays, it is a matter of grave concern and in future it will require a serious thought and concerted efforts to tackle it. This will requires uniform and swift handling at the national level instead of each one attempting in individual copyright.

7.0.2 Water Pollution

Eighty per cent of Indian population drinks polluted water from sources like lakes, wells and streams, over two million persons die of entric diseases every year, which are caused by drinking polluted water. Millions of people living alongside rivers which are the sources of water to drink, to bath and to wash dirty clothes and to bath their cows and buffaloes.

Water pollution problem is related to surface water and ground water. The surface water is polluted worstly by discharge into it of raw sewage waste, industrial effluents, contaminated water of kitchen wash, bath, washing etc., which have varying 141 concentration of toxic pollutants. The plant nutrients and dissolved mineral matters of detergents, chemical fertilizers, animal and human wastes also aggravate the pollution problem by way of contributing to oxygen depletion and production of toxic materials through their decay and decomposition. Recently, radioactive wastes are also added in the list of pollutants. All these together render water unsuitable for aquatic organism and for human life. In the river near the cities, discharge of untreated domestic water has created havoc of pollution.

Water gets contaminated due to the physical, chemical and biological pollutants. The physical pollution brings changes in the water in regard to its colour, odour, taste and thermal differences which create special problems for the water authorities.

Odour and taste is due to chemical pollution which is becoming widespread specially in developed countries due to the micro-contaminants of organic and radio­ active nature. Pollution from industrial sources is thus expected to increase with the use of water for industrial purposes, althougth the quantity of waste water returned will still be low as compared to 142 industrialised nations. The comparatively higher temperature of Indian waters and the low level of summer flows combined with generally increased withdrawals can be expected to lead serious pollution problem. Water pollutants in major industries are given in Table XXXIV.

The major industries causing water pollution problem are distilleries, tanneries, textiles pulp and paper, dairies, antibiotics, oil refining, fertilizers, steel mills. One source of industrial effluent are the sugar mills and Khandsari units, all of which are located in the rural areas. These sugar plants use larger quantities of water in the operations and discharge of two type of effluents, cooler and condenser waters and wastes from spillage, scum leaks, the washing of equipments and production of room effluents from the boiler houses and wastes containing lubricants and oil from machinery. Various effects are experienced from these wastes. Acidic or alkaline wastes from cleaning operations and heat exchanges can be harmful to aquatic life because of their high concentration of salts. Suspended solids may cause 143 TABLE XXXIV

Water Pollutants in the major Industries

Distilleries Low PH, high organic content (very high BOD), colour and dissolved solids.

Tanneries High organic content, high salt content, high colour, large amount of precipitable calcium content and chromium. Textiles' : a) cotton High PH, sodium content, organic matter and colour. b) synthetic Low PH, high dissolved solids and toxic organics.

Pulp and Paper a) Pulp mills High PH, high colour, some dissolved and suspended organic matter and high suspended inorganics and large volumes of wastes. b) Paper mills High suspended solids (mostly fibre) medium BOD, colour. c) Board mills High suspended solids (mostly fibre) medium BOD, colour.

Dairies High BOD, high colloidal solids, high rate of biodegradation, greases, acids or alkalies, odour on stagnation.

Slaughter Houses High BOD, colour, offensive odours on stagnation, iron.

Antibiotics High acidity or alkalinity, toxic, organics.

Synthetic drugs High acidity or alkalinity, toxic 144 organics

Organic chemicals High acidity or occasionally high alkalinity, toxic metals and salts.

Oil refineries Petroleum oils, emulsion or soluble from acids, alkalies, salts, phenols, soaps and resinous or tarry materials.

Fertilizers a) Nitrogenous High PH, ammonia content resulting in toxicity to fish and scorching of plant roots when used for irrigation. b) Phosphate High flouride content

Plating shops High acidity and toxic metals or

high alkalinity and cyanides.

Steel mills a) Coal washeries High suspended solids mostly cool & ash. b) Coke ovens High PH, and ammonia, high monohydric phenols and its derivatives and some cyanides and cynates. c) Blast High suspended solids mostly furnaces mineral oxides. d) Pickling shops High acidity and iron salts

Source : Sastry, A.C. and pitchai, R., "Water Pollution" in Benjamin, K.M.S. (ed.), Dimension of Environment With Reference To Conditions In India. Centre for Human development and social change, Madras, 1982. 145 blockage in drains and ditches and organic pollutants

(sugar and carbohydrates) can lead to the rapid exhaustion of oxygen supplies in streams causing foul odour and making the stream unsuitable for fish and other aquatic life.

It has been observed that fish are killed every year, a few days after the beginning of the crushing season in the month of May, June and July when the factory machines are cleaned and washed. The problem of water pollution due to discharge of domestic sewage has already become a serious problem in certain areas.

Though water pollution caused by domestic and industrial wastes is more readily apparent, the equally serious pollution caused by run-off from agricultural fields draining fertilizers, pesticides and insecticides is also increasing.

Pollution from industrial sources is thus expected to increase as the use of water for industrial purposes increases. Although, the quantity of waste water returned will still be low as compared with industrialised nations, the comparatively higher temperature of India, low level of summer flows combined with generally increased withdrawls can be 14b expacted lead to serious pollution problem.

The rainfall in India is generally limited to four months in a year, many of the rivers dwindle their flow

from December onward and are practically dry druing

summer when the demand for water is highest and pollution is accute. Nearly all the industrial centres have thus become the source of pollution problem.

Thus, the drinking water crises in the cities has

reached expolosive proportions. For years, urban dwellers have been silently suffering an intermittent

supply of poor quality of water. Most water supply

systems were installed decades ago for a small urban population. Today, they are old, badly maintained and grossly inefficient. In some cities, 20 per cent of water is wasted due to leakages, where sewage networks run alongside water pipes, there is cross contamination leading to epidemics. Industries are permitted to locate close to the water sources. Inadequate enforcement of water pollution regulations has inevitably led to contamination either by industrial pollutants or municipal wastes being discharged. 7.0.3 Land degradation

Thoughtless exploitation of the natural environment and unplanned industrialization and urbanisation have resulted in large scale degradation of land. Land pollution inevitably affects the health of man, higher animals and all other creatures that form delicate web of terrestrial life. Therefore, any- assault on the land in the form of pollution is an assault on the life.

Land has been degraded in almost all the countries even in the tropical countries through accelerated rate of soil loss by sill and gully erosion consequent upon rapid rate of deforestation. Large scale deforestation has resulted into the decrease of infiltration of rain water and therefore marked reduction in the recharge of ground water and have depletion in the ground water resources marked increase in surface run-off, accelerated rate of soil erosion through rainsplash, rainwash, sheetwash, sill and gully erosion decrease in agricultural productivity and gross agricultural output, changes in weather condition, increase in the frequency and magnitude of floods marked decrease in the biological diversity of the natural ecosystem and 14S

thus over all disequillibriam in the natural environment and ecological imbalences. Land has also been degraded by unscientific mining operations and accumulation of large amount of mining wastes and

industrial and urban refuse.

In general, land degradation problem can be grouped into following catagories :

a) Soil pollution due to city and industrial wastes. b) Soil pollution due to fertilizer and pesticides.

c) Soil pollution with man made chemicals. d) Soil salinity and alkalinity. Many types of

wastes are generated through different activities

in towns and cities. Some of these wastes which

cause land pollution are :

1. Domestic refuse originating from homes.

2. Refuse originating from hotels, institutions,

markets, stores, industries etc. consisting of :

a) Garbage : wastes from handling, storages,

sale preparation and consumption of food.

b) Rubbish : combustible and non-combustible.

c) Ashes from burning of fuels.

d) Street refuse; sweepings, leaves, dust etc. 149

e) Dead animals.

f) Night soil or human excreta and

g) Industrial refuse including solid wastes from

industrial, operations.

Solid wastes generated from domestic, industrial and agricultural sources. The quantity of wastes per person by domestic use varies considerably from place to place depending on the stage of economic and social development. Solid wastes of domestic origin may be incinerated, composted, dumped on the land, buried or disposed off in other way composting of open dumping may increase population of flies, rates and other vector of diseases. Buried organic wastes are subject to anaerobic decomposition and the production of methane and carbondioxide may result in pollution of ground water.

From time immemorial land has been treated as ultimate 'sink' for disposal of waste generated from human activities because of soil's ability to act as a filter physically (by sieving action), chemically (by absorption and precipitation) and biologically (by decomposition). However, with the triggering of process of industrialisation .and urbanisation the wastes being 150 disposed into the soil has undergone a qualitative and quantitative change resulting into saturation of carrying capacity of land. The sewage and sullage wastes mostly of city and industrial origin consist of a variaty of toxic inorganic chemical compounds which are potential hazards of environmental pollution particularly the heavy metals like mercury, lead, cadmium, nickel, copper, zinc, mangnese, etc. Which are extremely poisonous. The heavy metals reach the soil through these wastes and become part of life cycle of soil - plant - animal - man. Man being at the end of the food chain they accumulate in toxic levels creating several health hazards. Therefore, efforts must be made to drastically reduce the soil application of these toxic chemicals through sewage and sullage.

Chemical fertilizers, have been indentified as key input in present day agriculture. However, increasing level of fertilization has alarmed environmentalists, world over due to the potential danger of accumulation of residual fertilizer in ground water and other water reservoir leading to the problem of eutrophication. It is evident that fertilizer consumption in India is one 151 of the lowest and well below the world average.

Although, the average fertilizer consumption in India is very low, there is lot of variation from region to region ranging from 0.4 to 226 kg per hactare.

Literature is full of evidence that out of the total, fertilizer added to the soil hardly 50 per cent of it is being actually utilised by crops and considerable part of it goes to environment through deep percolation to ground water in case of nitrogenous fertilizer and through run off, soil erosion in case of phosphatic fertilizer.

Crop rotation system, traditionally practised in

India, for increasing soil fertility prevents the accumulation of pests and diseases in the soil. The use of additional fertilizers leads to the accumulation of injurious chemical constituents in the soil, which pass into the food web, where their effects may range from immediate to much more insidious long term. With advancement of production technology as protection technology has come up involving widespread use of a variety of pesticides. In the begining these pesticides were considered as wonder chemicals as they were found to be quite effective in controlling various diseases 152 and pests but within a few decade of their use the ill- effects of pesticides became evident.

First the majority of pesticides being non­ selective in nature kill the non-target group of useful, soil flora and fauna which is involved in important functions like nutrient cycling, soil development. Secondly, most of the pest develop resistance to the pesticides which either higher doses or use of new chemicals to replace those to which the pests are resistant. Thirdly, some of the pesticides are not easily biodegradable and hence, persist in the environment for years together.

However, the pesticides are necessary evil, we cannot avoid completely but efforts must be made to minimise the use of pesticide by alternative plant protection measures like use of resistant varieties, following crop combinations and cropping sequence which can prevent the built-up of pest population.

Chemical pollution of the soil results from unnoticed or incidental contamination of the soil with man-made chemicals. The pollutants can reach in soil through the ground water, the run-off of drainage water 153 and the plants used as food or forage for domestic animals and to a smaller degree through wildlife used as food.

The soil contains many inorganic and organic substances soluble in water. They are the products of weathering and decay of minerals and the degradation of organic water. Through microbial action these substances are normally oxidised to inorganic oxides but some organic compounds taking oxygen from ground water may not be fully oxidised. Human substances are found ever in the best water together with small amounts of so called trace-elements. During the last few decades, herbicides, insecticides, fungicides, soil conditioners and fumigants have resulted in the intentional alteration of agricultural, horticultural and silvicultural soil. The chemicals used may accidentally pollute the soil moisture.

The loss of top soil is a complex ecological problem and it is rather difficult to measure accurately its effect on crop yield and the mide array of interrelated factors that influence the productivity. Soil erosion is a serious drain on resource base despite the fact that the nature takes 154 about 100 to 1000 years depending upon the nature of parent material to form even 1 cm. of top soil. It has been estimated that about 6000 million tonnes of fertile top soil in India is every year, carrying alongwith it about 8.4 million tonnes of plant nutrients, which are more than what farmers are presently using annually as fertilizer (Kanwar, 1982).

It has been observed that housing alone in the urban sectors in India about 300 million tonnes of top soil are in danger of being excavated for brick making.

In view of the limited scope to bring more area under cultivation or extention of irrigation facilities to the extent possible is looked as only alternatives to increase gross cropped area. However, within a decade of introduction of irrigation soils have become saline and alkaline due to the accumulation of salts and have gone out of cultivation or lot of restrictions are imposed on the choice of crops to be grown on such soils. In India, about 7 million hactares of land is facing the problem of salinity and alkalinity. Together with this an additional area of nearly equal magnitude is affected by water logging and hence is facing the potential danger becoming saline and alkaline soils. 15o

In view of the seriousness of the problem the steps for prevention of soil erosion losses and better management of soil resources should get top priority so as to avoid any further disaster.

Thus in the present era of increasing population and technological advances in the field of agriculture and industries, soil resources are facing serious strains and stress because of mismanagement and neglect. Although the idea of zero-contamination is impossible, unrealistic and catastrophic to production of food and other goods, the necessary pollution can be and should be avoided by wise use of precious natural resources.

7.0.4 Noise Pollution

Pollution of noise is harmful to human system. In fact, noise is also a source of environmental pollution. In India, noise pollution is increasingly associated with urban life. It has been rightly observed that noise is a slow agent of death. The pivotal problem is to what extent noise can be said to voilate the golden rule of silence. No catagorical answer is available as it would vary from person to person, place to place, time to time, society to 156 society, function to function and from source to source.

The main sources of noise pollution are : various industries, mechanized construction and lawnmovers, fast moving automobiles and aircrafts. So these may be added periodical but polluting noise from sirens, loudspeakers, hawkers and a variety of festivity progremmes associated with community activities. Talks in gathering of friends, among office employees and on talephones also contribute to noise pollution.

In India, there is no law exclusively dealing with the problem of noise. The maximum decibel counts in some of the Indian cities is shown in Table XXXV. It may be seen from the Table that the metropolitan areas generate lot of noise, for example Delhi has a db of

89, while Calcutta ranking second has 87 decibels. The limit is high in other cities such as in Madras it is

89, in Bombay it is 85 and in Cochin 80 db respectively.

The sound level in industrial areas reaches its peak as industries do not follow the rules and standards fixed for maintaining acceptable noise levels in different regions. Industrial premises are the major 15/ TABLE XXXV

Maximtua Decibel covmt in Indian cities

Indian cities Decibel count

Delhi 89

Bombay- 85

Cochin 80

Madurai 75

Calcutta 87

Madras 89

Source K.P. and sinha, S., Noise Pollution Impacts

and control, Environmental Management. 1983. sources of generating high noise during their operations and thus resulting in damage to ears and creating a high risk environment to the people who are concerned with industries.

7.1 Review of studies conducted in Meerut and Ghaziabad districts

Maintenance of the purity and safety of the environment in the face of increasing urbanisation, industrialisation and machanisation of daily life is emerging as the most challenging problem facing mankind today. The huge quanitities of pollutants, solid 15S liquids and gaseous to which are being let out into the air, water and land system are investing the relationship between man and nature with new complaxities. Life support system in ecosystem are being strained almost to the point of no returns.

Some of the statistics pertaining to the environmental scenario are quiet revealing. At present mainly 70 per cent of the available water in India is polluted. Over 73 million workdays are lost annually due to the water related diseases. Every second about half hactare of forests is consumed for wood. In the last two decades in Delhi alone, there has been a tenfold increase in the number of automobiles pumping pollutants into air. No wonder, a breath of fresh air is becoming a rare commodity in the city.^

In developing countries, there are problem of industrial pollution because the countries are in a hurry to industrialise in order to meet the basic needs of their population. In industrial fields there are a number of pollutants such as gases, particulate matter and in social catagory there are domestic refuse and

1. Times of India, "Standards and environmental protection, Monday, 22 April 1991. 159 oboxious gases emitted from garbage, heaps and open drains. The most common pollutant today is the automobile exhaust which releases metals, metaloxides and poisonous gases like carbonmonoxide which reduces the oxygen carrying capacity of the blood stream.

Industrialisation has brought along with it the hazards of environmental pollution. This has gradually increased the concerned about the unplanned side effects which arise from releasing chemicals in the immediate surroundings. These chemicals from one of the major polluting sources which are discharged by industries without any care. In fact, metals primarily released by ores and processing of recycled metal products. When they are used in industries for the manufacture of various products or other articles they effect reaction came out as unwanted products and are released from industries without any dilution or treatment.

The industrial pollution has spoiled water air and soil. There is a long list of toxic material discharged from various industries. Various acid manufacturing discharge acid effluents which not only makes the land Ibf) infertile but also make the water of the river acidic.

The high acidity increase caused stomach diseases and skin ailment in the body.

Many industries releases S02 in the air as pollutant which on reaction with rain convert into sulphurous acids and get precipitated in the fields and rivers and thus destroy the vegetation and affect drinking water. There are some industries which discharge nitrogenoxides also in the air and so cause precipitation of nitrous acids in the fields and rivers which ultimately cause pollution. This pollution also causes respiratory disorders and other ailments of lungs and heart of human body.

Textile industries discharge alkaline effluents causing infertility of the soil and under the water useless for human being. They distroy the flora and fauna of the vicinity. Pesticides either contaminate the water by phosphate or chloride along with increase of BOD, COD, sulphates and nitrates. These are some pesticides which caused BOD even to the range of

20,000-30,000 mg/1. The dangerous pesticides such as

DDT, aldrin, dialdrin, hexachlor, benzene are harmful for the aquatic life and huamn being. I6i

The chemical industries discharge various toxic chemicals in the fields causing destruction of vegetation, soil and water. They should discharge effluent after proper treatment, otherwise the life on this planet will be difficult. For example in Meerut district, some chemical industries released even cynide which caused the death of 50,000 fish.

Fluoride industries discharged lot of fluoride in the fields without any treatment due to which people suffer from stomach ailments. Fluoride also reduce production in the fields. Metal industries discharge various metals and metallic oxides and thus cause pollution in air, water and soil. The toxic metals percolate in the ground water slowly and cause several diseases and mental disorders. Fertilizer manufacturing industries either discharge sulphurdioxide or nitrogendioxide in the air and both cause acid rain and destroy the growth of trees, fruits, vegetables and

9even grasses. The effluents of these industries are also harmful and must be discharge after proper treatment. The direct discharge of oil from oil industries affects aquatic life. It will be better to 162 TABLE XXXVI

Estimation of Pesticides present in Kali nadi at Meerut

Pesticides ug/1

1. a. Carbonate organiphosphorus 270

b. Chlorophenoxy herbicides

2. 2, 4, D. 38

3. 2, 4 TP (Silver) 60

4. 2, 4, 5, T 10

c. Chlorinated pesticide

5. Aldrin 5

6. Dialdrin 5

7. Endrin 2

8. Chlorodane 7

9. DDT 95

10. Heptachlore 0.3

11. Heptachlorepioxide 0.3

12. Lindane 15

13. Methoxychlor 2700

14. Toxophene 17.00

Source : Kudesia, V.P. & Singh, K.P., A profile of physico-chemical quality of Ganga river, Indian journal of Environment and agriculture. Vol. 3 & 4, 1989 . 163 review a few works conducted in Meerut and Ghaziabad districts relating to pollutants present in water bodies and atmosphere.

Some other studies conducted by [Kudesia, V.P.

(1987)], Table-XXXVI shows that pesticides present in

Kalinadi at Meerut. Hazandous substances are found in

Kalinadi and toxic metals at Modinagar in Ghaziabad district are given in Table XXXVII.

TABLE XXXVII

Toxic metals in Kalinadi at Modinagar, Ghaziabad distt.

Cu 3-7

Fe 2-4

Zn 6-8

Zn 2-3

Cd 1 p.p.m

Source : Kudesia, V.P., Water Pollution. Pragati Prakashan, Meerut - 1985.

Pesticides present in different food stuffs in

Meerut are given in Table XXXVIII.

Meerut is an industrially developed district besides being the most prosperous agriculturally advance district. Increasing industrial activities lead to pollution of environment in all respect. Pollution Ib4 TABLE XXXVIII

Pesticide Detection in different food stuffs in Meerut district

Food items No of Samples No. of samples found Analysed positive for pesticides

Milk 100 75

Spices 100 62

Fat and Oil 100 12

Spices 100 9

Cereals and pulses 100 83

Total food stuffs 500 241 from industries as well as sewage from the city and small areas increases the pollution of Kalinadi whose water is not suitable for irrigation purposes as the river has black and foul smelling water. The chemicals such as lead and cadmium and other insecticides not only affected the water cycle but also affected humidity. As a result the aquatic life in the river vanished and it also affected vegetable production.

A study conducted on the characteristics of textile industries of Meerut district revealed that textile industries of this region contain high 165 alkalinity and total dissolved solids which indicate that water is unfit for cattle, fish culture, vegetables, cereals and washing of cloths. It can caused skin diseases, stomach disorders and mental ailments if discharge directly into the pond on river used by human beings.^ Table XXXVIII shows that out of

500 samples of food items 241 items contains hazndous pesticides to some extent.

Another study has been conducted by (Kudesia,

V.P.) on the fluoride pollution in Pilkhuwa, an industrial centre of Ghaziabad which is badly affected by fluoride pollution. People of this area suffer from dental and bone diseases. Permissible limit of fluoride in water exceeds more than (1.5 ppm.) therefore, fluoride concentrate in different parts of the human body who reside at Pilkhuwa.

Regarding air pollution of meerut city, a survey has been conducted for 100 air samples at Begumpul crossing, one of the busiest crossing of the city and found that hazardous substances are present in the air.

Kudesia, V.P., characteristics of the textile industries of Meerut district. Water Pollution, pragati Prakashen, Meerut, 1985. 166

Table XXXIX reveals that carbodioxide, carbonmonoxide,

Nitrogenoxide, hydrocarbons and lead are found in the air of Meerut city area.

TABLE XXXIX

Air Pollution in Meerut city area (1991-92)

Hazardous substances Pure air (p.p.m.) 1991-92 (p.p.m.)

Carbonmonoxide 0 28-30

Carbondioxide 5 30-35

Lead 0 4 - 7 .

Hydrocarbons 0 8-12

Nitrogen oxide 0 3-5

Source : Kudesia, V.P., Air Pollution. Pragati Parkashan, Meerut, 1992.

Ghaziabad district of Uttar Pradesh is facing serious geo-environmental pollution and anthropogenic hazards. A study conducted by Geological survey of

India, revealed that lowing of ground water level owing to excessive withdrawl for agriculture and industrial purposes, besides excessive excavation of soil for the manufacture of bricks were also responsible for high grade pollution. 167

7.2 Industrial Pollution in Meerut and Ghaziabad

Districts

Meerut and Ghaziabad districts make a major industrial area of north-western part of Uttar Predesh.

The main industrial centres of the region are

Ghaziabad, Meerut, Daurala, Mawana, Dadri, Sardhana,

Moradnagar, Baghpat, Ghaziabad originally functioned under the Meerut Development Authority with the central functionary placed at Meerut, by from November 14, 1976 it was hand, over to G.D.A. Now it is the biggest and most prominent industrial area in the state. The major industries of the region are sugar, chemicals, distilleries, pulp and paper, textiles, pharmaceuticals, vegetable oils, sports goods and several others.

Industrialisation though having a positive impact on income-levels, employment and production economies has also brought with it many problems like shortage of housing, inadequate water supply, sanitation and waste disposal facilities, overcrowding and traffic congestion, air, water and noise pollution and an unsafe social environment. Thus the overall quality of 168 urban environment has deteriorated over the years with the increasing pressure on their infrastructure. Though the cities are considered as region of economic growth' but they contribute their role in unsustainable environmental terms. Today the concept of 'sustainable city has remained only on paper. Continued growth and expansion of existing industries, increasing use of transport system coupled with population growth in the urban areas is adding increased amount of pollutants in the atmosphere. Among the major pollutants in the environment those belonging to water and noise in

Ghaziabad and Meerut region are analysed here in detail.

7.2.1 Water Pollution

With the rapid increase in population as well as industries, the requirement of water is increasing. The use of water in homes and industries is increasingly affecting its purity. The main cause of water pollution in Meerut and Ghaziabad districts are discharge of sewage water and industrial waste water. All newly developed residential colonies of the cities make use of unpolluted underground water obtained through tubewells. There is, however, a small area of old city 169 where water is obtained from river Hindon. The river water is of course most polluted, because of uncontrolled discharge of domestic sewage and industrial effluents. The main site for discharge of toxic effluents are river Hindon Which passes through the city and river Yamuna situated on the western part of the city. The main industries which discharge their effluents into river Hindon are textiles, pulp and paper and board, distillery, chemical, metallurgical and processing work. According to the Pollution Control

Board, there are 16 pulp and paper board mills and-^ big distilleries which together discharge huge amount of waste water into water bodies. Among all distilleries

Mohan Meakins discharge the most toxic material which cause severe damage to the soil quality of the adjacent land. Mohan Meakins discharges about 1447 KLD of waste water which has pungent odour. This waste water is not suitable for irrigation. An increasing number of textiles, pharmaceuticals and other industries is causing serious environmental threat to the city of

Ghaziabad.

3 . Times of India, 'Ghaziabad district is highly polluted; November 25, 1991. 170

On the other hand in Meerut the main industries discharging their wastes into Kalinadi are the Sugar factories, distilleries, industries of modicomplex and

Khandsari untits. The volume of waste water discharged into the river from different sources varies from season to season. The industrial waste discharged from various industries has pronounced colour, which is imparted to the river water. The water of river Kali was found coloured in both summer and winter seasons.

The colour is more prominent and dark in this region during the winter season as it is crushing season for sugar factories. The colour of the stream ranges from light reddish during summer as in Meerut to dark brown in winter as seen in Hapur. The entire stretch of the

Kali nadi in district Meerut was found to be deficient in dissolved oxygen (DO) during winter. The high volume of bio chemical oxygen demand (BOD) of the stream were recorded at Meerut and Hapur in Ghaziabad in the winter and summer seasons showing high organic pollution in the river probably due to discharge of waste water from sugar factories, distilleries, Khandsari (Sugar) units, industries of Modi complex and sewage of cities situated along the river course. 171

There is considerable deterioration in the quality

of Hindon river at Ghaziabad where it recieves large

amount of city sewage and industrial wastes. The

gradual improvement in the quality of Hindon water may

be due to the merges of less polluted tributaries like

Kali West and Karsuni into Meerut district. Therefore,

Kalinadi is highly polluted at Meerut and Hapur.

7.2.2 Air Pollution

The main causes of air pollution in both cities

are emissions from automobiles, fumes and smoke

emitted from industries. The pressure of air pollution

has been monitored by Regional office of the Pollution

Control Board in Ghaziabad. Air samples were collected

from different part of the cities. In Meerut city, a

survey has been conducted on the crossings, the survey

has revealed that hazardous substances are present in

air around these observing stations. Important pullutants present in the city air are carbondioxide,

carbon monoxide, nitrogen oxides and hydrocarbons.

Besides these gaseous materials, high concentration of particulate matter was seen in new Kavi Nagar area and

Navyug Market (1996.43 mg/m^). This region has a 172 concentration of industrial establishment which have released large quantities of particulate matter in the air. As compare to it, Raj Nagar a purely residential character has the least ammount of particulate matter in the air.

7.2.3 Noise Pollution

The ill effect of noise vary from wild annoyance to irrevesible chages and permanent hearing loss. In addition to this, noise interference with communication system often causes accident,for instance at the level crossing it is an important factor leading to accidents. The main source of noise pollution in

Ghaziabad and Meerut districts are industries, automibiles and loudspeakers used at different occassions. Though the level of noise intensity have not been monitored till now but personal observations reveal that certain parts of the cities are very noisy.

The noisest area of Meerut city includes the main crossings of the city i.e. Begumpul crossing (Delhi-

Dehradun road), Baghpat gate crossing (G.T. Road),

Hapur stand crossing (Agra- Dehradun Road) while

Ghaziabad city includes Chopla Dasna Gate, Delhi Gate,

Sihani Gate and Jawahar gate (Navyug Market) Along G.T. 173

Road and Delhi-U.P. Border, this is because of the very high traffic intensity on G.T. road. In addition to this the shunting of Railway engines on the Railway lines passing through the main city create a high risk intensity of noise. The noise is deteriorated the hearing power and leads to intermitted sleep of the people living in near by localities.

Besides these residential-cum-industrial area also suffer from noise pollution. In Meerut city, powerloom functioning in most of the houses create high risk environment to the people residing in these houses, in the presence of loud noise of looms people are used to talk loudly which in due course of time affects hearing power.

7.2.4 Garbage disposal

People of these areas do not pay attention to properly dispose off garbage, ashes and other waste materials, instead they leave it on roads, outside their houses and on other public places. Solid wastes, left material includes garbages, ashes, rubbish, street sweeping, ashes, agricultural wastes and a variety of toxic industrial waste. Improper disposal of garbage 174 generally create problems to the residents of these areas. Only about 50 per cent of the total garbage is disposed off by the corporation /Municipal Board while the remaining portion remain there and endangers human health. The accumulating waste gives rise to a host of problems like contamination of water, soil and air, the proliferation of pests such as rodents cockroaches and flies and the consequent emergence of various forms of ill-health among the city's population particularly for those living in the vicinity of the dumps.

Waterborne diseases create a major problem in every rainy season when water logging takes place particularly in the low income settlements and causes contamination of water leading to a variety of water borne ailments. Cholera, dysentry and gastroenteritis claim many lives in these settlements every year. Open drains carry the untreated waste water to nearby rivers. The foul smell emanathing from the drains is unbearable and the polluted water in them creates an unpleasant sight making the life of urban citizen miserable. Sometimes people espacially of the poorer sections of the society are forced to use this water for washing and bathing thereby inviting various types 175

of skin diseases.

7.2.5 Social pollution

Growing industrialation is also the cause for

degeneration in the city's social life. Social

pollution is seen as a problem is these areas.

Attraction by better wages in industrial establishments

a large portion of rural population has migrated to

urban areas where in the absence of dwellings they

reside in slums along the roads and railway lines. Slum

dwellers live in unhealthy and unhygienic conditions

and give rise to many social problems. In Ghaziabad, "

the inadequate police force, rapid industrialisation

and increasing population particularly slum dwellers

and immigrant industrial workers, are turning this

industrial region into the " crime capital of North

India.1 Anti social elements have been increasing in number. Apart from these, other common problems of

industrial areas are kidnappings, daylight robberies

and labour militancy. All these unsocial activities have shettared the moral strength of the residents.

4. "From Industrial to crime capital", *The Hindustan times' , June 5, 1992. 176

CHAPTER VIII

CASE STUDIES : METROPOLITAN CITIES

8.0 The impact of industrialisation on environmental quality in the study region has been assesed by studying various aspects of pollution through the technique of factor Analysis in respect of habitat quality,land degradation, quality of life, air pollution, water pollution and noise pollution. The environmental pollution ultimately leads to several diseases that are damaging health of the people.

In the present study, two seperate Factor Analysis were conducted for Meerut and Ghaziabad districts.

Fi3?st step analysis deals with the city areas of Meerut and Ghaziabad. For detailed study, localities of metropolitan areas were selected as representative conditions prevalent in congested area, noisest area, residential area, industrial area and planned localities of the study region. The localities selected for determine environmental pollution in Meerut and

Ghaziabad cities are shown in Figure 17 & 18. Another detailed study was conducted after selecting 15 urban areas and small towns of the study region. These fifteen represetative areas were randomly selected from 177

SAMPLE STATIONS OF MEERUT OIYJ

INDEX == ROADS

BHOCR S><~~~ O 5A.MPLE STATIONS

FIG.17 178

all over the region for determining the impact of

environmental pollution in these areas. The areas which

were selected for detailed study in respect of habitat

quality, land degradation, quality of life, air

pollution, water pollution and noise pollution in

Abdullahpur, Mawana, Daurala, Baraut, Sardhana, Baghpat

and Kharkhauda of Meerut district and Babugarh, Hapur,

Dadri, Modinagar, Loni, Noida, Moradnagar and

Garhmukteshwar of Ghaziabad district.

8.1 In the first factor Anlysis environmental

pollution has been examined in respect of their habitat

quality, land degradation, quality of life, air

pollution, water pollution and noise pollution. An

attempt has been made to compare the environmental

conditions prevalent in both Meerut and Ghaziabad city

areas.

8.1.1 HABITAT QUALITY

Meerut city: Habitat quality is considered as an

important variable of environmental pollution. Factor

loadings concerning habitat quality in Meerut city are given in Table XL. Factor I of habitat quality explains

43.04 per cent of the total variance explained. This 179 TABLE XL

Habitat quality in Meerut city

Factor Variables Loadings Variance explained in %

43.04 Drains-flooding +0.93380

Foul smell +0.94861

Fumes/smoke +0.93419 II 32.87 Garbage spread +0.80886

Fumes/smoke +0.90286

Over crowding +0.80114 III 16.17 Garbage in heaps +0.96149

Over crowding +0.50064

Drains flooding +0.41346

Total variance explained 100.00 ISO I8i factor recorded an unclean environmental conditions owing to the problem of drains-flooding, foul smell and fumes/smoke as revealed by their positive loadings of

0.93380, 0.94861 and 0.93419 respectively. Factor II accounts for 32.71 per cent of the total variance and is strongly related to garbage spread (0.80886), fumes/smoke (0.90286) and over crowding (0.80114) in degrading habitat quality of Meerut city areas. The third step analysis reveals the impact of garbage found in heaps, over crowding and drains - flooding in deteriorating habitat condition with positive loadings of 0.96149, 0.50064 and 0.41346 respectively and explaining a variance share of 16.17 per cent.

Ghaziabad city: In Ghaziabad city areas, factor I of habitat quality explains 59.71 per cent of the total variance explained and is positively related to garbage spread, over crowding and drains-flooding as revealed by their loadings of 0.95728, 0.74061 and 0.42782 respectively. The second step analysis highlights foul smell (0.94121), fumes/smoke (0.92039) and over­ crowding (0.61943) as the main items in degrading habitat conditions of Ghaziabad city areas. Factor III is positively related to drains-flooding (0.89061) and 182 garbage found in heaps as the main contributing items in degrading habitat quality with a variance share of

10.58 per cent (Table XLI).

Comparison between Meerut and GhazieUsad cities

A comparison of Table XL and Table XLI reveals that in Meeirut city area owing to the drains-flooding, foul smell and fumes/smoke, general environmental conditions of environment is not clean in most of the localities as revealed by factor I analysis while in

Ghaziabad city garbage spread, over-crowding and drainsflooding are degrading habitat quality in factor I

In factor II, fumes/smoke and over crowding are the main problem in all localities affects habitat quality in Meerut and Ghaziabad city. Garbage spread is the problem of Meerut city while foul smell creates problem in Ghaziabad city areas.

The third step analysis reveals the impact of garbage accumulates in heaps and drains-flooding in degrading habitat conditions of Meerut and Ghaziabad city areas. Over crowding is creating problem in the localities of Meerut city. 183 TABLE XLI Hea)itat quality in Ghaziabad city

Factor Variables Loadings Variance explained in %

I 59.71

Garbage spread +0.95728

Over Crowding +0.74061

Drains flooding +0.42782

II 26.25

Foul smell +0.94121

Fumes/smoke +0.92039

Over crowding +0.61943

III 10.58

Drains-flooding +0.89061

Garbage in heaps +0.63864

Total variance explained 100.00 184

8.1.2 LAND DEGRADATION

Meerut city : It is clear from Table XLII that factor I of land degradation explains 44.76 per cent variance of the total variance explained in Meerut city. It highlights the role of various items in damaging land quality of this area. The hightest positive loadings is recorded by disposal of garbage on the street

(0.51152), improper garbage collection (0.50507) and domestic refuse (0.43198). Factor II accounts 20.04 per cent of the total variance. The main cause of land degradation in the city are domestic refuse that accumulates and degrades the land in these localities.

It recorded a high positive loading of (0.91752).

People generally dispose their garbage on the nearby streets as it recorded positive value of (0.69006) and irregular garbage collection ever after a week in some areas creates lot of problem and degrade land quality as it recorded positive value of (0.53338) . People also dispose their garbage in the nearby drain as revaled by their loading of 0.31946. The third step analysis reveals the impact of disposal of garbage on the streets and domestic refuse in degrading land quality of Meerut city as revealed by their positive loadings TABLE XLII 185

Land degradation in Meerut city

Factor Variables Loadings Variance explained in %

44.76 Disposal of garbage +0.51152 on the street

Garbage callected +0,50507 once a week

Domestic refuse +0.43198

Garbage collected -0.63680 from municipal collection sites

II 20.04 Domestic refuse +0.9.1752

Disposal of Garbage +0.69009 on the street

Garbage collected +0.53338 once a week

Disposal of garbage +0.31946 in the drain

III 19.03 Disposal of garbage +0.79099 on the street

Domestic refuse +0.61543

Garbage collected +0.31940 from nunicipal collection sites

Total variance explained 100.00 185 of 0.79099 and 0.61543 respectively factor III accounts for 19.03 per cent of the total rariance explained.

Ghazial>ad city : In Ghaziabad city areas, various items are positively 'correlated and thus degrading land conditions. Table XLIII shows that factor I accounts for 44.78 per cent of the total variance explained and is strongly related to domestic refuse and disposal of garbage on the streets as revealed by their positive loadings of 0.96506 and 0.82280 respectively. In few areas, garbage collected from the street (0.61940) but this collection process is quiet irregular factor II highlights the role of improper garbage collection, domestic refuse and in few localities industrial refuse in degrading land quality as revealed by their positive figure of 0.90067, 0.51840 and 0.31942 respectively. In some areas garbage is collected from municipal collection sites recording positive factor value of

(0.64190). Factor II explains 29.50 per cent of the total variance explained. The third step analysis reveals the impact of domestic refuse in damaging land condition of city areas recording positive value of

0.41939 with a variance share of 25.72 per cent. IS TABLE XLIII

Land degradation in Ghaziabad city

Factor Variables Loadings Variance explained in %

44.78 Domestic refuse +0.96506

Disposal of garbage +0.82280 on the street

Garbage collected +0.61940 from the street

Garbage collected •0.75449 from municipal collection sites

Brick bhatta •0.49751

II 29.50 Garbage collected +0.90067 once a week

Garbage collected +0.64190 from municipal collection sites

Domestic refuse +0.51840

Industrial refuse +0.31942 III 25.72 Garbage collected +0.95223 from municipal collection sites

Domestic refuse +0.41939

Brick bhatta -0.10941

Total variance explained 100.00 18S

Compasison between Meerut euxd Ghaziabad cities

A comparison of Table XLII and Table XLIII shows that in factor I domestic refuse is the main item of degrading land quality in both Meeirut and Ghaziabad city areas. People of these areas dispose their garbage on the street thus contributes a lot in land degradation. The collection of garbage through municipal authorites are quiet irregular in both cities thus creates a high risk condition in these areas.

In factor II there is slight difference in contributing items of land degradation of both cities.

The residents of both cities complain that garbage remain for a week on the streets creates problem and degrades land quality. The main item of land degradation is domestic refuse in each localities of

Meerut and Ghaziabad. In few areas industrial refuse degrading land quality in Meerut city while in

Ghaziabad people dispose their garbage on the street or in nearby drain.

Garbage is the main contributing item of land degradation in both cities. The collection of garbage took place through by municipal authorities in both

Meerut and Ghaziabad city areas. Generally, people 1S9 dispose their garbage on the streets in Ghaziabad thus degrading the land quality.

8.1.3 QUALITY OF LIFE

Meerut city: Quality of life is an important indicator

in determining the levels of living in different areas.

In Meeiait city, factor I of quality of life accounts

for 42.21 per cent of the total variance explained. It

is strongly related to shortage of electric supply

(0.95778), absence of suitable schools (0.79450) and lack of health facilities (0.76506) in degrading quality of life in these localities. On the other side, shortage of water supply and migration negativily associated to this factor as revaled by their loadings of 0.94499 and 0.69522 respectively. Factor II is strongly related to congestion/ lack of open space

(0.92143) and low income group people (0.86825) in degrading quality of life in these localities with a variance share of 26.10 per cent. Factor III accounts for 19.29 per cent of the total variance explained highlighting the role of lack of health facilities and shortage of water supply in degrading quality of life as recorded by their respective loadings of 0.46007 and IJO TABLE XLIV

Quality of life in Meerut city

Factor Variables Loadings Variance explained in %

I 42.21 Shortage of +0.95778 electric supply

Absence of suitable +0.79450 schools

Lack of health +0.76506 facilities

Shortage of water -0.94499 supply

Migration -0.69522

II 26.10 Congestion/lack +0.92143 of open space

Low income group +0.86825 people

Migration -0.31326

Unemployment -0.21467 III 19.29 Lack of health +0.46007 facilities

Shortage of water +0.31940 supply

Unemployment -0.31789 problem

Total variance explained 87.60 191 TABLE XLV

Quality of life in Ghaziabad city

Factor Variables Loadings Variance explained in %

I 50.11

Low income group +0.96631 people

Congestion/lack +0.83457 of open space

Lack of health +0.74105 facilities

Migration +0.63196

II 31.25

Absence of suitable +0.96490 schools

Shortage of +0.94139 electricity

Unemployment -0.72640

Congestion/lack -0.43766 of open space

III 13.14

Shortage of +0.98981

water supply

Migration +0.69888

Unemployment +0.3 8789

Total variance explained 94.50 192 0.31940 (Table XLIV).

Ghaziabad city: In Ghaziabad city areas low income group people, congestion/lack of open space, lack of health facilities and migration are the main contributing items in damaging quality of living recording positive loadings of 0.96631, 0.83457,

0.74105 and 0.63196 respectively. It is clear from the

Table XLV that factor I of quality of life accounts for half of the total variance explained. The second step analysis reveals the impact of absence of suitable schools and shortage of electricity with positive loadings of 0.96490 and 0.94139 respectively. This factor recorded negative factor values for unemployment

(0.72640) and congestion/lack of open space. Factor II accounts for 31.25 per cent of the total variance.

Factor III highlights the role of shortage of water supply (0.98981), migration (0.69888) and unemployment

(0.38789) in deteriorating quality of life in Meerut city areas.

Comparison between Meerut and Ghaziabad cities

It is clearly observed from Table XLIV and Table

XLV that there is slight difference in contributing items in degrading quality of life in both the city 193

areas of Meerut and Ghaziabad districts. The only item

that are common in both city areas is lack of health

facilities that are degrading life quality in Factor I.

Shortage of electric supply and absence of suitable

schools are the main items of degrading quality of life

in Meerut city, while low income group people,

congestion and migration are the main problem of

Ghaziabad city.

The second factor of quality of life highlighting

the problem of congestion/lack of open space and low

income group people of Meerut city, while in Ghaziabad

city areas absence of suitable schools and shortage of electricity are the main contributing items in degrading quality of life.

The third step analysis reveals the impact of shortage of water supply in damaging life quality of both the city areas. The other items that are playing their positive role in degrading quality of life are lack of health facilities in Meerut city, while migration and unemployment problem in Ghaziabad city areas. 194

8.1.4 AIR POLLUTION

Heerut city: Air pollution is an important variable of environmental pollution. Factor I of air pollution accounts for 47.97 per cent of the total variance.

Table XLVI shows that vehicular traffic (0.92004), waste disposal (0.86234) recorded highest positive loadings followed by coal burning (0.25100) and kerosene burning (0.16940) in degrading air quality of

Meerut city areas. The negative factor values marked by dead body burning (0.91042) and bhatta units (0.36795) in this factor. Factor II explains 26.65 per cent of the total variance explained and is positively related to waste disposal, vehicular traffic and wood burning with their positive share of 0.84714, 0.71948 and

0.51943 respectively. This factor also points negative factor values for dead body burning (0.25456) and coal burning (0.13696) reveals that they play their negative role in increasing air pollution in these localities of the city. Factor III highlights the role of waste disposal, coal burning, vehicular traffic and dead body burning in degrading air quality with positive loadings of 0.61941, 0.31940, 0.21480 and 0.14391 respectively.

GhazieOaad city : Factor I of air pollution explains 195 TABLE XLVI

Air pollution in Meerut city

Factor Variables Loadings Variance explained in %

47.97

Vehicular traffic +0.92004

Waste disposal +0.86234

Coal burning +0.25100

Kerosene burning +0.16940

Dead body, burning -0.91042

Bhatta units •0.36795

II 26.65

Waste disposal +0.84714

Vehicular traffic +0.71948

Wood burning +0.51943

Dead body burning -0.25456

Coal burning -0.13696

III 19.07 Waste disposal +0.61941

Coal burning +0.31940

Vehicular traffic +0.21480

Dead body burning +0.14391

Total variance explained 93.69 ISG TABLE XLVII

Air Pollution in Ghaziabad city

Factor Variables Loadings Variance explained in %

50.67

Vehicular traffic +0.98431

Waste disposal +0.61938

Coal burning +0.60263

Wood burning -0.59356

Dead body burning -0.41980

Bhatta units 0.31419

II 27.24

Waste disposal +0.74918

Vehicular traffic +0.64319

Coal burning +0.13494

Dead body burning -0.12496

III 20.24

Waste disposal +0.61944

Coal burning +0.14939

Vehicular traffic +0.10031

Dead body burning -0.41989

Total variance explained 98.24 197 half of the total variance. The main contributing items in degrading air quality are vehicular traffic, waste disposal and coal burning as revealed by their positive loadings of 0.98431, 0.61938 and 0.60263 respectively.

This factor recorded negative factor loadings for wood burning (0.59356), dead body burning (0.41980) and bhatta units (0.31419) . The second step analysis highlights the role of waste disposal, vehicular traffic and coal burning in degrading air quality of

Ghaziabad city. The only item recorded negative factor loading is dead body burning with value of 0.12496.

Factor II accounts for 27.24 per cent of the total variance. Factor III which explains 20.24 per cent of the total variance explained is positively loaded to waste disposal, coal burning and vehicular traffic as revealed by their factor loadings of 0.61944, 0.14939 and 0.10031 respectively.

Comparison between Meerut and Ghaziabad cities

A comparison of factor I clearly shows from the

Table XLVI and Table XLVII that main items in damaging air quality are vehicular traffic, waste disposal and coal burning in both city areas of Meerut and Ghaziabad 198 districts. On the other side, dead body burning and bhatta units play their negative role in spreading air pollution in Meerut city while wood burning, dead body burning and bhatta units are the items that are not generally performed within the city limit play negative role in Factor I.

In factor II, vehicular traffic and waste disposal again registered main items in damaging air quality of both Meerut and Ghaziabad city areas. On the other side wood burning is in practice in few localities of Meerut city while coal burning play a positive role in spreading air pollution in few areas of Ghaziabad city.

The third step analysis reveals the impact of waste disposal, coal burning and vehicular traffic in deteriorating air quality of both city areas of Meerut and Ghaziabad districts.

8.1.5 WATER POLLUTION

Meerut city : The result of the factor analysis for determining environmental conditions shows that in

Factor I which explains 46.68 per cent of the total variance explained. The contributing items in damaging quality of water in Meerut city are water logging, septic tanks/soak pits, waste water from houses and 19:) TABLE XLVIII

Water pollution in Meerut city

Factor Variables Loadings Variance explained in %

I 46.68

Water logging +0.93409

Septic tanks/ +0.83533 soak pits

Waste water +0.78324

Dairy animals +0.63190

II 38.96

Water logging +0.88844

Waste water +0.70702

Dairy animals +0.49441

Industrial -0.31984 pollutants

III 12.76

Waste water +0.63419

Water logging +0.41984

Dairy animals -0.69486

Industrial -0.41984 pollutants

Total variance explained 98.40 r\ 00 dairy animals recording positive loadings of 0.93409,

0.83533, 0.78324 and 0.63190 respectively. The second step analysis reveals the impact of water logging

(0.88844), waste water (0.70702) and dairy animals

(0.49441) in polluting water of the surrounding areas.

Factor II accounts for 38.96 per cent of the total variance. Factor III is positively related to waste water (0.63419) and water logging (0.41984) in increasing water pollution of Meerut city with a variance share of 12.76 per cent (Table XLVIII).

Ghaziabad city : The first factor of water pollution highlighting several positively correlated items that are playing their role in increasing water pollution of

Ghaziabad city areas. Factor I accounts for 50.96 per cent of the total variance explained and is positively related to waste water (0.98436), septic tanks/soak pits (0.64980), water logging (0.43196) and industrial pollutants (0.31940). The second step analysis reveals the impact of dairy animals, water logging and industrial pollutants in increasing water pollution with loadings of 0.43194, 0.31849 and 0.21948 respectively. Factor II explains 23.69 per cent of the 201

TABLE XLIX

Water pollution in Ghaziabad city

Factor Variables Loadings Variance explained in %

I 50.96

Waste water +0.98436

Septic tanks/ +0.64980 soak pits

Water logging +0.43196

Industrial +0.31940

pollutants

II 23.69

Dairy animals +0.43194

Water logging +0.31849

Industrial +0.21948 pollutants Septic tanks/- -0.14378 soak pits

III 15.52

Industrial +0.41984

pollutants

Water logging +0.31976

Dairy animals +0.21976

Total variance explained 90.17

» 202 total variance. Factor III is positively related to industrial pollutants (0.41984), water logging

(0.31976) and dairy animals (0.21976) with a variance

share of 15.52 per cent (XLIX).

Comparison between Meerut and Ghaziabad cities

It is clearly observed from Table XLVIII and Table

XLIX that water logging septic tanks/soak pits and waste water from houses are the main, items of spreading water pollution in both city areas of Meerut and

Ghaziabad districts. Animals kept for dairy purposes play their role in increasing water pollution in Meerut city while industrial pollutants are positively correlated in Ghaziabad city in factor I concerning water pollution.

The second step analysis highlights the problem of water logging and dairy animals in polluting water of both Meerut and Ghaziabad city areas. Waste water from houses polluting the environment in the localities of

Meerut city while industrial pollutants are playing their positive role in spreading water pollution in

Ghaziabad.

In the third factor, water logging again registered as the main source of water pollution in 203 both city areas of Meerut and Ghaziabad. Waste water from houses also playing their role in damaging water quality in Meerut city while industries pollutes the water quality in Ghaziabad district.

8.1.6 NOISE POLLUTION

Meerut city : Factor I of noise pollution is positively related to traffic and loudspeakers in

Meerut city areas. Vehicular traffic registered as the major source of noise recording positive loading of

(0.74346) . Loudspeakers used at various functions generate noise in the localities of Meerut city with positive value of (0.61942). Factor I explains half of the total variance (Table L) . Factor II of noise pollution is strongly related to vehicular traffic in generating noise with a value of 0.94694 while loudspeakers recorded low factor loading of 0.31469 with variance share of 31.40 per cent. The third step analysis also reveals the impact of loudspeakers and traffic in generating noise with positive loadings of

0.41384 and 0.12946 respectively. Factor III accounts for 14.99 per cent of the total variance explained.

Ghaziabad city : The results of the factor analysis TABLE L 204

Noise pollution in Meerut city

Factor Variables Loadings Variance explained in %

50.79

Traffic +0.74346

Loudspeakers +0.61942

II 31.40

Traffic +0.94694

Loudspeakers +0.31469

III 14.99

Loudspeakers +0.41384

Traffic +0.12946

Total variance explained 97.18 205 TABLE LI

Noise pollution in Ghazizdaad city

Factor Variables Loadings Variance explained in %

54.70

Traffic +0.85191

Loudspeakers +0.34617

Industries +0.10965

II 26.72

Traffic +0.74946

Loudspeakers +0.61396

III 16.58

Loudspeakers +0.31941

Traffic +0.21665

Total variance explained 98.00 206 concerning noise pollution in Ghaziabad city areas shows that the major sources of noise are traffic, loudspeakers and industries. Factor I is positively related to traffic, loudspeakers and industries in generating noise as revealed by their positive loadings of 0.85191, 0.34617 and 0.10965 respectively. Factor I account for 54.70 per cent of the total variance. The second analysis highlights traffic and loudspeakers as the main sources of noise pollution recording positive loadings of 0.74946 and 0.61396 respectively. Factor II explains 26.72 per cent of the total variance. Factor

III again registered loudspeakers (0.31941) and traffic

(0.21665) in increasing noise of Ghaziabad city with a variance share of 16.58 per pent (Table LI).

Comparison between Meerut and Ghaziabad cities

It is clear from Table L and Table LI that in both city areas of Meerut and Ghaziabad noise is generally produce due to the vehicular traffic and loudspeakers used at various functions creating problem for the residents of these localities.

In factor II and III traffic and loudspeakers again registered as the main source of noise in both city areas of Meerut and Ghaziabad. The noise generated 207 due to these sources creating high risk conditions for the people residing nearby affected areas and they complain about several problem due to noise pollution in which headache, irritability, nausea and problem of hearing are the main problems for both the city areas of Meerut and Ghaziabad districts.

POLLUTION RELATED DISEASES

8.1.7 Water borne diseases

Meerut city : Environmental pollution leads to the spread of several pollution related diseases that are degrading health of the people. In Meerut city, water pollution results in various water-borne diseases.

Factor I of water borne diseases explains about half of the total variance explained and is strongly related to diarrhoea (0.95214), jaundice (0.91279), throat infection (0.69647), other diseases (0.67667) and dysentry (0.52080) [Table-LII]. Factor II is strongly related to cholera (0.93403) and dysentry (0.77976) as the main water related diseases that affects health of the people residing here. Factor II accounts for 39.81 per cent of the total variance explained. Factor III highlights kidney stone (0.92217), dysentry (0.34744) 208 TABLE LI I

Water borne diseases in Meerut city

Factor Variables Loadings Variance explained in %

49.62

Diarrhoea +0.95214

Jaundice +0.91279

Throat infection +0.69647

Other diseases +0.67667

Dysentry +0.52080

II 39.81

Chloera +0.93403

Dysentry +0.77976

Other diseases -0.68368

III 7.81

Kidney stones +0.92217

Dysentry +0.34744

Throat infection +0.30748

Total variance explained 97.24 209 TABLE LIII

Hater borne diseases in Ghaziabad city

Factor Variables Loadings Variance explained in %

48.96

Diarrhoea +0.92253

Other diseases +0.82257

Kidney stones -0.57238

II 28.78

Jaundice +0.91779

Throat infection +0.65736

Cholera -0.85401

III 23.30

Kidney stones +0.79762

Throat infection +0.60636

Dysentry -0.91390

Total variance explained 99.04 2i0 and throat infection (0.30748) as the main diseases with variance share of 7.81 per cent of total variance explained.

Ghaziabad city Factor I of water borne diseases explains about half of the total variance explained and it highlights diarrhoea and other diseases as the main diseases of this region as revealed by their loadings of 0.92253 and 0.82257 respectively. Kidney stone is the only disease that recorded negative loading of

(0.57238). The second step analysis reveals the impacts of jaundice and throat infection in degrading health of the people of Ghaziabad city areas with positive loadings of 0.91779 and 0.65736 respectively. In factor III, kidney stone and throat-infection recording positive values of 0.79762 and 0.60636 respectively with a variance share of 23.30 per cent (Table-LIII).

Comparison between Meerut and Ghazisdsad cities

It is clearly observed from Table LII and Table

LIII that various water related diseases are positively correlated in Factor I. The main diseases that are degrading health of the people are diarrhoea and other diseases in both city areas of Meerut and Ghaziabad districts. Jaundice, throat infection and dysentry are 211 the outcome of water pollution in the localities of

Meerut city area.

The second step analysis reveals the impact of cholera and dysentry on the health of the people of

Meerut city while in the localities of Ghaziabad jaundice and throat infection are the main water related diseases that are degrading health of people.

Factor III highlights the role of kidney stones and throat infection in damaging quality of health of the people residing in both city areas of Meerut and

Ghaziabad districts.

8.1.8 AIR BORNE DISEASES

Meerut city : Air pollution through various sources leads to several related diseases in Meerut city. Table

LIV shows that factor i accounts for 55.33 per cent of the total variance explained and is strongly related to asthma (0.96295), headache (0.75912) and nausea

(0.70365). Factor II of air related diseases highlights bronchitis and eye-irritation as the main diseases that are degrading health of people residing in Meerut city areas as revealed by their positive loadings of 0.94254 and 0.93278 respectively. The third step analysis is 212 TABLE HV

Air borne diseases in Meerut city

Factor Variables Loadings Variance explained in %

55.33

Asthma +0.96295

Headache +0.75912

Nausea +0.70365

Skin diseases -0.84142

II 26.19

Bronchitis +0.94254

Eye irritation +0.93278

Nausea -0.67836

III 15.87

Other diseases +0.98921

Headache +0.47088

Skin diseases -0.43848

Total variance explained 97.39 213 TABLE LV

Air borne diseases in GhaziaJaad city

Factor Variables Loadings Variance explained in %

48.43

Bronchitis +0.97551

Nausea +0.92758

Eye irritation +0.57157

II 26.17

Skin diseases +0.92454

Other diseases +0.61347

Headache +0.46769

III 16.07

Asthma +0.92840

Headache +0.85692

Eye irritation +0.52277

Total variance explained 90.67 214 positively related to other diseases (0.98921) and headache (0.47088) with a variance share of 15.87 per cent.

Ghaziabad city : Factor I accounts for 48.43 per cent of the total variance and is strongly highlights the role of bronchitis and nausea in damaging health quality of the people residing in the localities of

Ghaziabad city. It recorded positive loadings of

0.97551 and 0.92758 respectively. The second step analysis positively correlated skin diseases (0.92454), other diseases (0.61347) and headache (0.46769) as the main air pollution related diseases of the localities of Ghaziabad city areas. Factor II accounts for 26.17 per cent of the total variance explained. Factor III is strongly related to asthma, headache and eye-irritation as revealed by their positive share of 0.92840, 0.85692 and 0.52277 respectively. Factor III accounts for 16.07 per cent of the total variance explained, (Table-LV).

Comparison between Meerut and GhazieO^ad cities:

It is clearly observed from Table LIV and Table LV that factor I of air borne diseases highlight nausea as the common problem in both city areas of Meerut and

Ghaziabad. Factor II recorded positive role of 215 bronchitis and eye-irritation in damaging quality of health of the people residing in Meerut city while skin diseases and headache are the main diseases that are positively correlated in the city areas of Ghaziabad district. The third step analysis recorded positive impact of air pollution on the health of the people in the form of headache in both the city areas of Meerut and Ghaziabad districts. 216

CHAPTER IX

CASE STUDIES : SMALL TOWNS AND URBANS AREAS

The impact of industrialisation on environmental quality has been assessed by studying various aspects of pollution through second factor analysis in respect of habitat quality, land degradation, quality of life, air pollution, water pollution and noise pollution in selected towns and urban areas of the study region. The environmental pollution through various sources leads to several related diseases that affects the health of the people residing in these areas. The areas selected for detailed study are Abdullahpur, Mawana, Daurala,

Baraut, Sardhana, Baghpat and Kharkhauda in Meerut district and Babugarh, Hapur, Dadri, Modinagar, Noida,

Moradnagar, Loni and Garhmukteshwar in Ghaziabad district (Fig 19)

9 .0 ABDULLAHPUR

Abdullahpur lies at 28° 59' North latitudes and

11°AS' East Longitudes on the road passing from Meerut to Parrichatgarh and is about 5 kilometers of Meerut between Abu Nala and Kali-Nadi (east) . Abdullahpur was a town area uptill 1981 when it had a population of 6383

(1981 census). In 1991, it merged with Meerut municipal 21

T

o u.

l_ 218

board. Handloom cloth is manufactured in. the town by

the local weavers.

Habitat quality

Factor I of habitat quality recorded an unclean

environmental conditions in Abdullahpur owing to the

problems of over-crowding (+0.99347), fumes/smoke

(+0.98687), garbage found in heaps (+0.90924) and

drains-flooding (+0.77436) explaining a variance of

53.71 per ceiit. Factor II reveals the impact of foul

smell, garbage spread and drains - flooding in

deteriorating habitat condition with positive loading

of +0.99523, +0.92325 and +0.63274 respectively and

explaining a variance share of 26.22 per cent. Factor

III in strongly related to foul smell (+0.94731) and

garbage spread (+0.64310) and accounts for a variance

share of 20.07 per cent. The factor loadings of each

factor are shown in Table LVI.

Land degradation

It may be seen from Table LVI that domestic refuse and brick bhattas are the main items of land degradation in Abdullahpur as revealed by their positive share of 0.99977 and 0.97496 respectively in 2] ' CO ;9| 1 en i-l O 00 'T CO CO o 00 o 00 1 C m rH o 1 r- cn rH ^ rH rH o t^ 00 ' -H r^ m o 1 O rH cn cn •* 1 00 cn cn cn cn 1 O P 1 "D ^ r-l 1X1 •* rH 00 1 UD •"J" rH r-i ro 1 fN 1 1 m CTl U3 vr 1 O cr\ VD in r^ U3 in •V rH 1 n 1

+ + — 1 ^.

.y 1 H OJ 1 H 0) i-H 1 H (0 a CO It) -rl OJ >, 1 K U -H >i OJ rH 1 O u o M-l r-i (0 Qi tn r-< D H r-i tX O 0) 4-1 E lO IH U-l rH W r-H U ,-< 4J rH o 3 C 0) 0 (U 0 0) l*-l V (0 •D O x: E e 0) U x; •H 0) 0 OJ w Cn !0 •H OJ XI OJ JJ IW 0)U 01 It! C 4J Ui Dl U 0 ID c 10 ^ .-H ja -rH tn 10 M ID 0) 4J -rl 4J D V^ 10 OJ £> U -Q rH M >-l IH o 10 IH B u •H U r-i u o 3 O a a, o D O 10 iH 10 O 10 x: 0 X •H Q CO U U ••q CO iJ CO t- — • ^ — o 0) in (N tn •^' CO o (M ro •* «• 00 CO CM t)i n fN vji 111 CO r-l •H r~- (N rN o r~ tN r~ C tn n fN U) fM r-l m rH ro CM rH fN rH co in 1 iH •H m (N n rH • CTv 00 u> u> rH U5 O O in r- 1 o^ a> VO >T CTv CTi IJ3 cn U> in in 'f M-l 10 00 O 1 0 0 o o o o o O O o CNJ O o o o rM 1 HJ + + + p + + + 1 + + 1 1

.c 4-1 •H c rH ' o H 0) E & . : H x; tn H j-i ID OJ >i 1 > •0 ' Oi 0) -H N OJ O c U tn 4-1 rH a 1 •H •rl •H a ; H •H 4J a a 1 u !/l s OJ rH U 0 3 I U < 1) 0) 4J 0) •H •H OJ tn 1 t^ b. (—1 cn u U U a a0 ! XI (0 -D 4J 10 U 'H 1 ra tn XI 0) tn IH u a o 1 •H •H fn a (U iH 4J 0) 3 4J 1 J-) U •D c 10 tn 10 u 0) .C f-^ 0 to It) (0 •H tU D Dl OJ 4J OJ 3 1 4) x; u > TD x: •-< rH Dl (0 0 OJ i-H 10 IH lu 1 r-H CX O C VJ o o c OJ o 0) C 1 nH U) r-H -H u 0 x; E 0) >iH U rH OJ o O 0) e OJ (L> •rH ID OJ OJ IH Dl U cn •0 tn Oi tn tn 4.) tn Dl Dl o ID c 10 1 (0 c 10 tn ID ID 4J •rH 4J 1 rH XI •H ,Q OJ o c XI XI (H U 1 X) D VJ It) u E tD.-n HID IH IH U 0 2 0 O ID >H 10 O •H IH ID 10 ID JZ 0 ci. o Q O Q Q "D O 'h-i^ TT •s— - H o m

tn c~ t^ ^ 1^ rH r- in vc o tn 1/1 U) (N ro KC C~. • 4J c i< CO (N m t~ r~ rH 0^ CO fH rH rH t-- r^ CN rv: • •H •r-l ro 1.0 a\ ^ en 00 • :- in cn cn rH in cn cn 00 r-- cn CO • 0 • • 00 0^ r J o o o o o o o o o o in O o o c o •SI I & ; + + + + 1 + + I 1 + •f •f — -t + + ' 4J ' OJ OJ tn m ; -C -C 0) tn ID 4J 4J 01 o\» 1 •H 1 o\o 1 C OJ •H r^' >- • o\° 1 0) c C W 1 CJ a - ' H 1 C > U •rl O C 1 a a •rH Cl< •-' c • • H r C C 1 -H 1 o 0 rH 3 '- •H ' U ' 0 0) OJ O 1 OJ •H tn — 1 0 1 XI 1 Dl Dl •H 1 TD ! UH a u '^ 1 n < 4J 1 01 r n ID 10 C 4-1 1 OJ 1 o ID SH _ ' a > 1 U 1 m 1 tn ' C 1 z 0) Xi XI •rt U 1 C 1 Ci •rH > g ^3 r-H in 1*H E U 1 X < ^^^ ID U^ <^- 1 X • I, D 3 J^ C 0 O ' «C IH u o 0 o D flj 1 b c 0) 01 0 Z • O 1 n; ' a O 0 H r—1 ' K m o "O r~i 1 O 0 e j= i W E U, 1 d) 1 o u JZ r-l rH ID 1 OJ 1 -H 0 C 0 ' OJ ' > ' H U tn 01 U 1 u •H X) 0) ID ID OJ a 1 U 1 4J u IH D^ r ' U 1 « < ~\ 01 tn 1 C 1 Q OJ Dl W tn 4-1 Dl •H 1 C 1 t: tn c 0 ID IC ' C 1 1 y w IS C 1 m > W .V (0 O corn 0 U ' « 1 H 3 (0 W 1 10 1 IC O u (0 QJ -H M -H 4J 1 W Q a O S Q "0 Q to o E 1 > 1 O U tn •J J CO W ! > 1 220

Factor I which explained a variance share of 58.20 per cent. In few areas garbage is not collected for a week and remains on the street thus degrading land quality of the surrounding areas with positive loading of

0.97496. Factor II explains 28.12 per cent of the total variance explained. The highest positive loading is shown by domestic refuse (0.99140) and garbage collected twice a month (0.66183) which play an effective role in degrading land quality. Factor III accounts for 13.68 per cent variance and highlights the role of domestic refuse (0.96194), weekly garbage collection (0.64918) and brick bhattas (0.51948) in deteriorating land condition of Abdullahpur.

Quality of life

Factor I explained 59.15 per cent of the total variance. It reveals the importance of various items like congestion/lack of open space (+0.93916), low income group people (+0.86672) and lack of health facilities (+0.74973) in degrading quality of life in

Abdullahpur. The second step analysis highlights the role of lack of health facilities and shortage of electricity which affect quality of life in these areas and recorded positive share of 0.66174 and 0.50128 221 respectively. Factor II accounts for 20.75 per cent of the total variance. Factor III explained 20.20 per cent of variance and reveals the impact of various items in degrading quality of life in Abdullahpur. The highest positive loading in this factor is shown by lack of health facilities (0.64918) and shortage of electricity

(0.51900) (Table LVI).

Air pollution

Factor I of air pollution recorded a variance share of 47.80 per cent. Table LVII shows that wood burning (+0.98148) and vehicles (+0.92745) recorded highest positive loadings followed by bhatta units

(+0.78757) in degrading air quality of Abdullahpur.

Factor II accounts for 32.16 per cent of the total variance explained and is strongly related to vehicles and waste disposal with their positive share of 0.37394 and 0.98646 respectively Factor III which explains

20.04 per cent of the total variance explained is positively loaded to vehicles (0.64519) and waste disposal (0.61398) in deteriorating air quality of this region. U) m en 00 n 00 0 0 (N cn en c I-! en Tj< ^ rH ••J" ro rH -r-* in rn \D (Ti t- rH U^) VD n in 222 Ti T}< rH tN ro cn m cn en U) in U) U) TH rH vo •

o H 4J U tn • rl << u •H XI E M u V^ en c (U • C (U (0 -H >i 4-) C (0 M rH •0 3^ "O (0 10 4J 10 D JQ 0 3 0) CJ ^ U 0) X3 •H •H ij "O -d tan MH £ Kh 0 n3 4-1 u •a MH S OJ (0 0 0) w 3 (0 S S Q 0 iH > a •J £H •H (0 (0 0)

01 VO -c* 00 ro (saN 0 wC O rn in cn Pi 01 I* en t~- 00 VO CM cn 00 rH rv) c U) n tn en 'J' in 0 •a" cn in o •H 00 r- • M< r- cn rH -H TS en r^ en a> cn en cn 00 cn cn 3 O 0000 0 0 0 0 0 0 •J + ' t ' + t O O4 0) w •H H o H > o tn •d a El tn OJ m CO '-< l-l W c rH a tn tn 0 xJ D -u )H a XI -H ^ c 0) w u C y. o • M fO 0) D •H 4-1 in T3 rH C u a; 0 01 ra 4J U •H a (U 0" to 4J u >, cn -H tH tn W -rl 0 u iH D U IW •O en ^ U (0 4-1 •H ri a (0 3 (3 C/ 0) x: (0 « CQ S Q M W H rJ

d oD in n r- CO 0 0 CD n cn o C TT ^ 00 Ln c- CN m in rH in -H r-i r- m r- c^ OC (N m CO en 00 •! 3 0 0 10 4J 0 •r* aj 04 rH 2 (c0 1H u O X! O H OJ aj x; (0 to (0 tl! (0 0 IH c to < 2 > Q CQ s s s LO u a H M > 223 Water pollution

The result of the Factor Analysis for determining environmental conditions shows that in Factor I which recorded 51.70 per cent of the total variance explained rain water producing water logging (+0.99778), waste water from houses (+0.88920) are the main items spreading water pollution in Abdullahpur. Factor II explains 31.30 per cent of the total varicance explained. The highest positive loading is shown by rain water producing water logging (+0.99462). Factor

III accounts for a variance of 17.00 per cent and highlights the role of waste water and dairy animals in polluting water of the surrounding areas recording positive loadings of 0.69710 and 0.43140 respectively.

Noise pollution

Factor I accounts for 56.10 per cent of the total variance explained (Table LVII). It is strongly related to vehicular traffic as the major source of noise with a value of (+0.92213). Constant noise leads to many diseases and people complained about headache, nervous system disorders and irritability. The second step analysis also registered traffic as the only contributing item in generating noise in Abdullahpur 22i with high positive share of (0.97415). Factor II explained 32.15 per cent of the total variance. Factor

III accounts for 11.75 per cent of the total variance explained and highlights the noise generating loudspeakers used at various functions and traffic with values of (0.99636) and 0.46319 respectively.

Pollution related . diseases

In Abdullahpur, environmental degradation leads to the spread of various pollution related diseases. Air pollution in this area leads to several related diseases as given in Table LVIII. Factor I accounts for

56.10 per cent of the total variance. Skin diseases

(0.99939), headache (0.99677), asthma (0.97078) and eye-irritation (0.94831) are the main diseases that affect the health of the people. Factor II accounts for

31.75 per cent of the total variance and is strongly associated to nausea (0.99987) and bronchitis

(0.99398). Factor III explained 12.15 per cent of the total variance. It highlights headache and nausea as the main diseases with strong positive loadings of

0.94100 and 0.74198 respectively.

Water pollution of Abdullahpur results in various 225 TABLE-LVIII Pollution related diseases in Abdullahpur Factor Diseases Loading Variance explained in %

Air-borne diseases I 56.10 Skin diseases +0.99939 Headache +0.99677 Asthma +0.97078 Eye-irritation +0.94831 Other diseases -0.91919 II 31.75 Nausea +0.99987 Bronchitis +0.99398 Eye-irritation -0.31734 Headache -0.23997 III 12.15 Headache +0.94100 Nausea +0.74198 Asthma -0.46194 Other diseases -0.12948

Total variance explained 100.00

Water-borne diseases I 48.70 Throat infection +0.99778 Typhoid +0.99778 Diarrhoea +0.88920 Cholera +0.54130

II 31.30 Jaundice +0.98121 Cholera +0.84083 Kidneystones -0.99420 Dysentry -0.96595

III 20.00 Typhoid +0.68145 Diarrhoea +0.51980 Cholera +0.41976 Kidneystones -0.13494

Total variance explained 100.00 226 related diseases. Factor I of water borne diseases explained 48.70 per cent of the total variance. This factor is strongly related to throat infection

(0.99778), typhoid (0.99778) and diarrhoea (0.88920).

Factor II highlights jaundice (0.98121) and cholera

(0.84083) and expalined a variance share 31.30 per cent of the total. Factor III is strongly related to typhoid

(0.68145) and cholera (0.51980) as the main water related diseases that are damaging the health of the people residing here. Factor III accounts for 20.0 per cent of the total variance (Table LVIII) .

Svunmary

The above discussion makes it clear that foul smell and garbage spread are the main problems of

Abdullahpur in degrading habitat quality. Waste disposal and vehicles pollute the air to some exjbent which create headache and nausea. Waste water from houses and water logging also create problem, as a result of water and air pollution several diseases prevalent in this area e.g. diarrhoea, dysentry, typhoid, jaundice, nausea, bronchitis and headache are the common diseases of this region. Vehicles and loudspeakers are the main sources of noise resulting in 227 irritability to the people of the region. Domestic refuse and brick bhattas are the main causes of land degradation while congestion, lack of health facilities and shortage of electricity are degrading quality of life in Abdullahpur.

9.1 MAWANA

Mawana town lying at 29°06' North latitudes and

77°56' East longitudes is situated at the junction of many roads. A high metalled road connects it to Meerut which lies at a distance of about 26 kilometers. Other roads from Mawana lead to Hastinapur, Parrichatgarh,

Phalauda and Behsuma, This place is also called Mawana kalan to distinguish it from Mawana Khurd, a village lying 6 kilometers to the west.

Mawana is a municipal board and had a population of 57644 in 1991 with 27291 males and 24353 females.

The population recorded a growth rate of 37.28 per cent from 1981 to 1991. The town is located in an important sugar cane producing region and therefore a sugar factory has been established here. The town is also known for its handloom industry. Habitat quality "*'"

Factor I of habitat quality explained about half

of the total variance. It is strongly related to

garbage found in heaps (0,95587) fumes and smoke

(0.44160) are degrading habitat conditions in Mawana.

Factor II reveals the impact of over crowding,

fumes/smoke and drains-flooding in degrading habitat

quality with positive loadings of 0.984a6, 0.89230 and

0.57248 respectively explaining a variance share of

30.41 per cent. Factor III is strongly associated to

foul smell (0.99957) and drains-flooding (0.55931) and

accounts for 17.24 per cent of the total variance

explained. The loadings of each factor are given in

Table LIX.

Land degradation

It may be seen from Table LIX that Factor I of land degradation explains 56.24 per cent of the total variance explained. It highlights the role of industrial refuse, garbage collected once a week domestic refuse in degrading land quality of Mawana as revealed by their respective values of 0.99632, 0.97375 and 0.78881 respectively. Factor II of land degradation accounts 35.07 per cent of the total variance explained 2i% in t-1 r^ V£< CO 00 rH in cn in no m rv) rH en CT^ vX) ^ O U) tH cr^ iT\ CTi v U) o I-* -D >^ ro CM 00 CTv Ln LD 1^ o rH I^ fM 1 cn iH -^ •sf r^ ID T5 crv LD in CJA r~ U) (N rH 1 U> trs ^ ro 00 U3 o o o o o o o o 1 CO o o o o 1 1 1 1 1 .(. 4- ^ 1

(U d u •H (0 cn to rH l-l to atn CO O u lU >, o i) C -H •-t s: c C u 0) 4J a u o 0 4J -H a-H a tn H •H (U 3 0 rH D u tl) (U -H tn tu «; c(Un cr Ij 14H U rH (0 IT) 4J T3 O 10 IH XI CO J3 XI tn 0) H-l 0) 10 CD a 1-1 u tl 4-1 JJ 4-) C ro (0 <0 cn tu u ^U £ lO -H -H (U Dl Dl 3 £ tu 10 U 3 D -O £ 4J rH rH cn U-l 14-1 (U rH •^ (0 14-1 m o o 0 c 0 c tu O I+-I PI rH O C 0 U o x: o i-l rH -H rH -H (1) 0) m (0 O •H 0) tu iJ l»-l cn i) B cn tn u i-> cn Dl CO O 10 U w tn Di O 0 ID tn ID ID x: j •r^ -H U o H3 ID 0 o ID x: XI > O >-i IB Q Q Q U HP CO < -H ti, Q O m u o e 0) >4-l h -H VD o 00 o i~- CO U3 00 t~- rH in U3 0-1 n •tr in o o cn CM O 00 c V (N fN o o in CD CM \D en 00 o CD a\ r~ in CO *H •sr t-- CM IM r-- t-~ ro o T3 ,J= r>.H ( U H m u 4-1 U QrrH *-> •H y •H in a a o 41 I c U D 0 to Dl cn u Dl ID U 10 C 4J •O tn c to 03 CD X ID 4-1 C 4-1 -H ID > 1-1 (1) •H XI XI iH u XI iH CU iH 1H a il F ta 1-1 i-i .H •H i~ O tn O 3 cn Id D M (D to 0 1-1 ID x: o -H o> Uu Q o CJ) u oa C! C/D '3, w ^ s:

>1 X [^ o f^ n fN in (H C- ro o CO ^ f^ C7> ^ •H 0- • 00 U) tN in m t^ 00 00 in ro ID O (Tl tN U) rH Z ' Ln tH kD CTl U3 m 00 c- r- OJ tH rH in ro 'J' Id IS)

•H OJ c a u c a c 3 o tu o cn tn ; U E U (0 Z X) 1-1 3 e tn r-i ID 1 iH 3 Dl 0 lu u 1H iC Hw * 13 a ro 1^ C (0 0 -H c u iH 1 ID D -H i: C 10 ID M 33 Q T3 1 O C>u O Q o 03 Q D 0 > c/i D J > 230 and it recorded brick bhattas as the main source of land degradation with loading of (0.31518). Factor III is strongly related to disposal of garbage on the street (0.70611) and domestic refuse (0.61097) with a variance of 8.69 per cent of the total variance explained in this region.

Quality of life

Factor I highlights the role of in-migration and shortage of water supply in degrading the quality of life in Mawana as revealed by their positive values of

0.97168 and 0.33104 respectively with a variance share of 51.32 per cent of the total variance explained.

Factor II accounts for 36.02 per cent of the total variance and reveals the impacts of items like shortage of electricity (0.92208) and absence of suitable schools in degrading quality of life. The third factor highlights the role of congestion, lack of health facilities and shortage of water supply in deteriorating quality of life with their loadings of

0.91448, 0.44301 and 0.34265 respectively. The factor loadings of each factor are given in Table LIX. 231 Air pollution

Factor I of air pollution recorded a variance share of 59.32 per cent. Table LX shows that vehicular traffic (+0.86400), Bhatta units (+0.70592) and coal burning (+0.59836) are the main sources of spreading air pollution. Factor II explained 25.95 per cent of the total variance and highlights the impact of waste disposal, bhatta units and vehicular traffic as the main contributing items of increasing air pollution recording positive values of 0.98454, 0.70592 and

0.61319 respectively.Factor III which explains 14.73 per cent of the total variance explained is positively- loaded to vehicular traffic (0.83419) and waste disposal (0.78542) in degrading air quality of Mawana.

Water pollution

Factor Analysis of water pollution in Mawana shows that Factor I is strongly related to rain water producing water logging (0.99967). Industrial waste water (0.95431) and waste water from houses (0.43164) with a variance share of 46.47 per cent of the total variance explained. Factor II accounts for 44.05 per cent of the total variance and shows the impact of septic tanks (0.94405) and waste water from houses CA CN •* 'S' in fv) f»i C-- 00 01 rH •^ •* 1-4 00 00 CN in ON C ^ in iH <3< 00 o 23'2 •H ro 00 tN r^ ^ in rH U3 •V CN 00 C^ cri •^ 0^ 00 O 0^ (N n o o o o o o + + 1 ' * •f

H H H en 0) o CO 3 O x: E IM •H O >W r-l C (0 (0 u Vl CO 01 3^ •4-1 0) Dl CO 4-) 0 C 0 u rH C ^ a-H 1) (0 -H 0) ^1 CO C 4-1 e 01 J^ (15 w N -H Ol 0) (0 -H M Tl (0 m rH T3 3 c o 01 a iH n 3 10 rH u £1 3 XI S3 •H a (0 U 0) >.VH UH CO •H •H 4.) T3 T) »H > 3 S Q S Q S H J •H a o in r>> M cr\ Ov ID in o in rH o •H 01 l/l CTl rH rH O CT\ CT\ m CO JJ c 1' ui m m> i-l ^ ir\ ro r~ a\ •H 00 O rH rH O • o •H M H a o u 0) 10 s •H •H c o M-l r-1 14-1 c CO M (0 10 u CO iH (U to CO u 3 m to iH rH 0 Jj 4-1 J3 c u O 0. •H •H c (u e OJ la CO u >, d (0 4J -H PI •H •H c 3 (0 "O >H u 10 C 10 VJ T) rH 3 0) U U (0 (0 3 X()I XI u d-H > (U Jj O •H (U >, to I4H d) 4J 4J •H T) rH iJ 4.1 IH 73 IH CO (0 x: in m a CO -rl 3 10 (0 a Q o CO 3 a J E-" a o m o fs VD vo t~- rH ^ IS [^ 9< rH m CO t^ U} o o^ a\ cn in ro rH Tl 00 t^ in (Tl a» a> I* c^n 0^0 r>j •-• (0 iH O o o o o o o O o O o

1 -»• 1 O + + + •t- •t- -t- ^• Oi M •rl CO •4: V m CO jj 3 H «c i:n: OS u 4J O •H 01 3 F- c » rH O r-t M o IT) Ho 01 MH H ^ o U u en e B a m H 4J iJ c 3 n •r« u u u g* (fl •rl •rl J3 ti 01 rH 0) 0) tA H) U 0) g iH C »j 01 10 4J t3 a (U (U >-l »:) 10 3 u IH •H et cn (0 H M c •H 4J rH f) i) 3 4J •rl W TJ I4H 3 (0 M Bt C (0 (0 V4 U T3 CO H 3 H n (U >< in C m (0 O O U C (0 ^ > OQ O « SE 2 M s > a ij £-> M > 233

(0.93068) in deterioraing quality of water of Mawana.

The third step analysis reveals the impact of waste water (0.94185) and dairy animals (0.85182) in polluting water of the surrounding areas with a. variance share of 9.48 per cent of the total variance explained. (Table LX).

Noise pollution

Factor I of noise pollution accounts for 71.77 per cent of the total variance. It recorded a high influence of loudspeakers (0.94332) and vehicular traffic (0.84817) in increasing noise pollution in

Mawana. Factor II concerning noise pollution explained a variance share of 14.92 per cent. It is positively related to loudspeakers (0.52731) and traffic (0.31980) as the main contributors in increasing noise in this region. Factor III accounts for 13.31 per cent of the total variance explained and highlights noise generating role of traffic (0.96857) and loudspeakers

(0.24098) used at various functions in this region. The loadings of all items are given in Table LX.

Pollution related diseases

In Mawana, pollution through different sources 234 TABLE LXI

Pollution related diseases in Mawana

Factor Diseases Loading Variance explained m %

Air-borne diseases I 61.14 Headache +0.97485 Other diseases +0.94620 Skin diseases +0.81677 Nausea -0.13697 II 32.01 Eye-irritation +0.98926 Nausea +0.57871 Asthma -0.96626 Other diseases -0.32163 III 6.85 Skin diseases +0.54795 Asthma +0.25752 Nausea -0.77376 Ete-irritation -0.10268

Total variance explained 100.00

Water-borne diseases I 52.85 Throat infection +0.99967 Dysentry +0.95431 Jaundice +0.93068 Other diseases +0.43176

II 25.12 Cholera +0.94405 Typhoid +0.90942 Diarrhoea +0.32990 Kidneystones -0.40395

III 22.03 Diarrhoea +0.94185 Kidneystones +0.85182 Typhoid +0.40454 Jauadice +0.35805 Cholera -0.25363

Total variance explained 100.00 235 leads to several pollution related diseases in this region. Air pollution in Mawana results in various diseases as given in Table LXI. Factor I accounts for

61.14 per cent of the total variance explained.

Headache (0.97485), skin diseases (0.81677) and other diseases (0.94620) are the main diseases of this region. The second step analysis reveals the impact of air pollution in the form of eye irritation and nausea that are positively associated with loadings of 0.98926 and 0.57871 respectively. Factor II explained .32.01 per cent of the total variance. Factor III accounts 6.85 per cent of the total variance and it highlights skin diseases and asthma as the main air borne diseases with positive loadings of 0.54795 and 0.25752 respectively.

Water pollution of this region also results in several water-borne diseases in Mawana. Factor I explains 52.85 per cent of the total variance explained. It shows the positive impact of water pollution in the form of throat infection (0.99967), dysentry (0.95431), Jaundice (0.93068) and other diseases (0.43176) that affects the health of the people residing here. Factor II accounts for 25.12 per cent of the total variance explained. It is strongly 236 related to cholera (0.94405) and typhoid (0.90942) in degrading health of the people. In the third step analysis, Diarrhoea, Kidneystones, Typhoid and Jaundice

are the positively related diseases with a variance

share of 22.03 per cent.

Summary

The factor analysis of various aspects of pollution in Mawana clearly shows that environmental

conditions of this area are not clean due to the presence of fumes/smoke, foul smell and drains-

flooding. The main sources of air pollution are vehicles, bhatta units and waste disposal. As a result, various related diseases are common among the people.

The major sources of water pollution are water logging and waste water from houses. Water pollution of Mawana give rise to diseases as dysentry, throat-infection, jaundice, cholera and typhoid. Loudspeakers and vehicular traffic are the main sources of noise which directly affects the health of the people. Domestic refuse degrades land quality in Mawana while in- migration, shortage of electricity and absence of

suitable schools are responsible for damaging quality 2'M of life in the town. *•"* 9 .2 DAURALA

Daurala town located at latitude 29'>07' North and longitudes 77°43' east lies on the western side of

Meerut-Saharanpur highway, it is situated about 14 kilometers away from Sardhana and enjoy the facility of a railway station on the Delhi-Saharanpur section of the Northern Railway.

Daurala had a population of 9716 in 1991 with 5180 males and 4536 females. Its commercial importance increased with the establishment of a sugar factory in

1932 which is well known for its cube-sugar.

Habitat quality

Factor I of habitat quality accounts for 55.92 per cent of the total variance explained. Factor I recorded an unclean environmental quality as it strongly related to foul smell (0.98895), garbage in heaps (0.77295), over crowding (0.58101) and fumes/ smoke (0.31009).

Factor II highlights the impact of garbage spread, fumes/smoke and over crowding in degrading habitat quality of Daurala as revealed by their positive loadings of 0.92316, 0.91735 and 0.11154 respectively.

Factor II explained 24.17 per cent of the total 238 variance. The third step analysis with a variance share of 19.91 per cent is strongly related to garbage spread 0.9906 and over crowding 0.62459 in deteriorating habitat conditions in Daurala. (Table-LXII). Air Pollution

Factor I accounts for 46.90 per cent of the total variance explained. The major items that play their role in spreading air pollution in Daurala are waste disposal (0.97796), vehicular traffic (0.92182) and wood burning (0.87078). Factor II reveals the impact of vehicular traffic (0.97765) and waste disposal (0.95496) in spreading air pollution with a variance share of 31.09 per cent. Factor III which explains 22.01 per cent of the total variance explained is positively related to waste disposal 0.99334 and vehicles 0.29523 in deteriorating air quality of Daurala. Water Pollution

The result of the Factor Analysis for determining environmental conditions shows that in Factor I which recorded 62.09 per cent of the total variance explained. Dairy animals (0.97638) and waste water from 239 01 kO CT\ "^ O rH 'S" fl r- in 00 T-I o in en o CD rn ,H tN 00 o r~i 1X1 ro 00 r- r- o -tj" r^ r- VXl in o 00 TH

0) t H 01 U H •fH (0 01 r-i H c ft (0 3 0] 01 o (0 "O E N 0) o C rH -H x; >, O 01 U 01 01 ft JJ U JJ e 01 -H H U 0) 0 01 ft ft-rl 0 3 rH O c > iH JJ u o 01 l*H •H 01 -rl 0) -H 01 tH tj rH iH T3 0 U to X3 JJ lU 0) 0) c 01 14 10 U CJl 0) iJ JJ JJ 0 ji«; JJ JJ 01 •a c 01 u u u -H u 10 x: •rl rH 3 01 0) 01 JJ 10 3 JJ 3 01 Id 00) Ol-H iw rH r-l rH u <-l r-l 01 U -H O >! OJ rH rH 1-1 01 -^'n ta U-l CO U 0 rH C O 01 IJJ O n) axj o o U rH CO 3 0 x: 0 U u O u o 0) •M •H 01 U1 in •sr 00 in in o in <(< 03 in m N rH m in •<»< in CO U} n in (N o^ IX) o c n t~ .H CO 00 O O) •<]< u> P> rH > [-- r^ O T) en en r-l 00 a\ 00 tN en 1X1 CT^ C\ CN o 10 O o o o o o o o o o O O O o >i + + + I 1 + + + 1 JJ + + + •H cH M 0) m 01 01 3 & 10 u (0 (0 o H •a H 01 o H a H c 01 01 u x: ft X -H u u •rl u (0 c c 3 01 3 tN O o 0 JJ 01 JJ I a t-i CJl -H H o U ro T) T) n ^J U •H XI 0) 01 01 X3 01 -H JJ Dl u 4-1 JJ JJ (0 JJ U •a 10 U u o JJ 10 JJ 9 ID t-i (d 01 X) 01 01 •H 0) m Dl tn U 1 01 01 Dl Dl JJ u m (0 (0 lO 01 O c m j<: nj £ 10 £ 10 c JJ JJ (U £i u B 01 (0 M -H u c U C Dl 01 n o -0 lO 3 •H ^j (0 M (0 o 10 O x: x; a C3 b. Q T3 O OQ C3 E o e w w

>1 JJ CO 1/1 m H •H 00 CO rH tJ CQ ID O 10 Q JJ Oh^ KJ c/D O 01 D B. o 6 £ > Q O > > 240 houses (0.73767) are the main items of spreading water pollution in Daurala. Factor II explains 24.18 per cent of the total variance and is strongly related to rain water producing water logging (0.88981) and industries

(0.54760) in polluting water of the surrounding areas.

Factor III accounts for 13.73 per cent of the total variance explained and highlights the role of industries and waste water from houses in degrading water quality of Daurala as revealed by their positive loadings of 0.44098 and 0.43079 respectively. (Table-

LXIII).

Noise Pollution

Factor I accounts for 65.01 per cent of the total variance explained (Table-LXIII) . It is strongly related to loudspeakers (0.94877) and traffic (0.93869) as the main source of noise in this region. The second step analysis also registered traffic and Loudspeakers as the main source of noise in Daurala with positive loading of 0.94877 and 0.93869 respectively. Factor II explains 28.84 per cent of the total variance explained. Factor III accounts for 6.15 per cent of the total variance explained and it highlights the role of traffic and loudspeakers in generating the role of tn ^ (TV 00 rf 00 CTl Cft l^ cr> en Di ro m LD cn en r- f- C- o >-i c n in r-l in o o o •* en •* 241 •H cri cri •"J* o ^ ro n •sr 03 m T3 £r> CO CO 1/1 •a* >3> n CM rH in (0 ^ O o o O o o o o o o o + + 1 1 + + 1 + + 1

H H H

OS o H a •H U C a ut-l CO CO 01 U Id 3 OJ iJ M-l TJ 3 • TJ CO (0 3 T) s CO fH J M •H

d CO in «5 in 1" rH o c~ r~ o> o o C51 VO 1T\ CT( en CO Vi5 CO t~ u> <3< •H r- "J" (N r- CT\ C^ a\ 00 00 O c t- in 00 CO 00 r-l •o* m l-H a\ c^ 00 in CO i«n• in tn CO 0 •a o> ro (0 o o o o O o o o d) O o 0 + + ) t + + ' + + I cu

H o H H H H a CO Oi u •o o c a H a (d < •H m 3 M PI >M o ••^ r-l •cH -H (0 (0 c 01 0 s jj M M CO M (V C ft CO Q) U u 3 c u s» UX) •H 0) CO XI v< m C O) (0 4J >i 0) la (B •H V u O -H 10 la T-i O r-( tl 7) Oi V U Oi 3 (cU J3 •H U ii 01 H CO 0) tn i»-i w •H U O T3 0) 3 u TJ iw 3 01 U 4J T) tn 3 I0T3 > x(U: 0) n lO C 10 O U C m n SMS « > S !«S S r3 H M

d CO uo (N 00 r~ ^ r- o\ CVJ o en in -H c r- H o ^ i-i l£) r- U} 00 00 'I" •H t~ fM t»- 'I' 00 r- n r» •f ro (N •o C^ r-

•n TJ 0) c c c 8 •r^ a •H r-4 >« g (0 o fO (0 10 •H 09 01 rH -H .-H 0a CO u 01 0) 01 *1 -1 c U •w u c 4J C 3 ai a ca •u () •H •H -H 0) A B (U 01 a to a H H 4J 01 X H^ ^ j 3 m u > > > 242 traffic and loudspeakers in generating noise in Daurala as revealed by their positive figures of 0.34476 and

0.28909 respectively.

Land degradation

It may be seen from Table-LXII that brick bhattas, domestic refuse, garbage collected once a week are the main items of degrading land quality of Daurala in

Factor I which explained 46.33 per cent of the total variance explained. Factor II accounts for 33.15 per cent of the total variance explained and it highlights the role of improper garbage collection and brick bhattas as the main items of land degradation as revealed by their loadings 0.80085 and 0.28260 respectively. Factor III accounts for 20.52 per cent of the total variance explained. The highest positive loadings is shown by domestic refuse (0.61621) and garbage collected once a week (0.52584) which play an effective role in deteriorating land quality of

Daurala.

Quality of life

Factor I explains 55.98 per cent of the total variance. It reveals the impact of various items like 243 low income group people (0.94483), lack of health facilities (+0.91559), shortage of water supply

(+0.72956) and congestion/ lack of open space in deteriorating quality of life in Daurala. Factor II accounts for 31.45 per cent of the total variance explained and is strongly related to migration

(+0.99728) and absence of suitable schools (+0.98195) that are degrading quality of life. Factor III accounts a share of 12.57 per cent of the total variance explained and is positively related to congestion/ lack of open space (+0.96165), shortage of water supply

(+0.62938) and lack of health facilities (+0.39281).

(Table-LXII).

Pollution related diseases

Environmental pollution of Daurala results in various pollution related diseases that are degrading health of the people residing in these areas. Air pollution of this region leads to several diseases. In

Factor I which accounts 51.33 per cent of the total variance explained is strongly related to bronchitis

(+0.99967) and eye-irritation (+0.92907). Factor II explains 38.22 per cent of the total variance explained

Nausea and headache as the main diseases of this factor 244 TABLE-LXIV

Pollution related diseases in Daurala

Factor Diseases Loading Variance explained in %

Air-borne diseases I 51.33 Bronchitis +0.99967 Eye-irritation +0.92907 Other diseases +0.54833 Nausea -0.15676 II 38.22 Nausea +0.95673 Headache +0.93974 Skin diseases -0.90114 Eye-irritation -0.23414 III 10.45 Skin diseases +0.42982 Asthma +0.35978 Headache +0.30181 Nausea -0.01166

Total variance explained 100.00

Water-borne diseases I 59.82 Kidneystones +0.97638 Dysentry +0.77644 Diarrhoea +0.73767 Cholera -0.71111 II 33.10 Jaundice +0.99761 Throat infection +0.88981 Diarrhoea +0.51987 Typhoid -0.36971 Cholera -0.32300 III 7.08 Typhoid +0.90591 Diarrhoea +0.43079 Other diseases +0.67520 Cholera -0.54112

Total variance explained 100.00 245

recording positive loadings of 0.95673 and 0,93974

respectively. Factor III highlights skin diseases,

asthma and headache as the major air borne diseases with loadings of 0.42982, 0.35978 and 0.30181

respectively. It explained 10.45 per cent of the total

variance explained. (Table-LXIV) .

Water pollution of Daurala results in various

related diseases. Factor I of water pollution accounts

59.82 per cent of the total variance. This factor is

strongly related to kidney stones (0.97638), dysentry

(+0.77644) and diarrhoea (+0.73767). Factor II highlights jaundice (+0.99761), throat infection

(+0.88981) and diarrhoea (+0.51987) and explained a variance share of 33.10 per cent of the total. Factor

III positively associated to typhoid (0.90591), diarrhoea (0.43079) and other diseases (0.67520) as the main water related diseases that are damaging the health of the people residing here. Factor III accounts for 7.08 per cent of the total variance. (Talbe-LXIV).

Siunmary

The factor analysis of various aspects of Daurala shows that environmental conditions of Daurala are not 246 clean owing to the presence of garbage spread, fumes/ smoke and flooding of drains that are degrading habitat quality. The main sources of air pollution are waste disposal and vehicles which lead to several air borne diseases in this region. The major sources of water pollution are dairy animals, waste water from houses and rain water producing water logging. Water pollution also results in giving rise to several water related diseases, the important ones being kidney stones, diarrhoea, dysentry and typhoid. Traffic and loudspeakers are the main sources of noise leading to headache and irritability amongst the inhabitants.

Domestic refuse as well as brick bhattas are degrading land quality while shortage of water supply, congestion/ lack of open space, low income group people degrading quality of life in Daurala.

9.3 BARAUT

Baraut, a municipal board of district Meerut is situated at a distance of about 41 kilometers to the north-west of Meerut at 29°6' North latitudes and ll°ie' East longitudes on the Sardhana (Delhi)

Saharanpur road. Other roads join it to Binoli in the east, chhaprauli in the north-west and kotana in the 247 west. This town is bounded by eastern Yamuna canal on the west and by Miranpur distributory on the north and east.

Baraut witnessed 46.19 per cent rise in population between 1981 and 1991 and presently (1991) has a population of 67693. This town is famous for manufacturing of wheel rims, axles and motor springs.

Habitat quality

Factor I accounts for 56.19 per cent of the total variance explained. It recorded an unclean environmental conditions owing to the problem of garbage spread (0.93118) and over crowding (0.59768).

The second step analysis reveals the impact of foul smell (0.91930), fumes/ smoke (0.83138), over crowding

(0.72389) and garbage spread (0.25058) in degrading habitat conditions in Baraut with a variance share of

34.66 per cent. Factor III is positively related to drains-flooding and over crowding as revealed by their positive loadings of 0.91750 and 0.34463 with a variance share of 9.15 per cent (Table-LXV).

Factor I accounts for 58.62 per cent of the total variance explained. Table LXV shows that Factor I is en Oi 1 o ro in VD CT> 00 rH 01 00 rH 00 c in !,£> a\ \0 r-^ r-i ^ rH Ol 'I" cn ;248 •H r- •tj* CM rH ^ ro rH T! 1- •"T ro \0 (N >H CS ro ^ CN <3< (D cn n n 1 f t- r-l iH iH VD ro rH rH ( 1 1 O o o o o o o o o o o O + + 1 + + + 1 + + + 1

x: u c 6o rH tn (0 r-l (Odd O m nj -H >, O OJ o 0) -H U ^ JZ •'-1 >N H O (H -H a u i-l iJ O •<^ 73 C Q, cn -H -ri 3t 3 3 "-H U tn 0) -H • H ^> •cw e rH U tH m n c tH XI to i-l cn a : u •H k > (0 E M JH ^H rH o tn u o u o u O (0 <0 (0 O x; fl (0 x: Q O a CD U CO ^ H3 1 1 cn

o 00 cn 00 cn rH tt> o ro cn uj rf r^ r-{ 01 ro n CO in rH t— CTv r~ tjt o cn <• ^ t~ C (Ti rH ro o << 5J« CM VO vo u> o U3 U> C^ •H iH m r\) in GO cr> o cr\ o t~- r- t- O 1^ o T3 iTi CO t^ CN) t cn t3< T3< Ol cn «;}* ^ cn cn i^ 1 (0 o o o o o o o o o o o o o o O + + + + + + + 1 + + + 1 1 1 -H + — x; i-l (1) u & c0 to tn e ij arH C 4) tn tn O 10 -H 01 S H r-l -H >, C X! 0) ^J J-l a iJ iJ (U U M o u TD tn a-H -H a D rH U a tn o o c0 C C tn -H -H o (LI •rl •H O a u •M rH 9 •a VH lO iJ O XI 4J M -H j<; T) a O -H iJ -H O 0) O C t-l H) o r-H M n 3 m 1 U T3 10 T3 x: •d (U f= o x: H) 0) > e 0) ^ OJ 0) (U XI (U OliW D1 i°.°tJ (U O •d CO ^-^ O Dl 01 D1 01 to o to tn O rH tn CO to ID A: (0 iJ i-l tu c a ^ ai tl XI XI XI CJ XI >H Jii in 01 (u e 3 e 0) >H W ^^ -H VJ O U O c to (u o l2 O CD to 10 U 10 x: to x: o ^ d C3 o m o tfl J cn U «5 D

X? w •H 00 CO vo cr> o o r< vD •* CT\ O O •* rH in in H c rH VT) cri o t^ [^ CN O rH p- TJ" •* O rH (^ ro i-l cn M< ui VO in (71 rH •H r- VD cn oi cn in CM CN •a m a» tit r-l <» Ol rH VD CO t>- r~ 00 r- CM CM in n cn Ol 00 in cn 00 CO r- u> q< «t< Id o o o o o o o o o o o o o o o o o + + 1 r 1 + + H- 1 + + + + + + 1 to C (0 tn 0 Id -H 0) o >. (0 ID 0) -H >l X: rH 4J U U i-H iJ •H 04 •O -H a-H urH tun aa O 3 O -1 O 3 c H C u 0) -H rH (u tn •r( •3 •H U rH TJ a oto J-l XI >H (U tx to i-H (U at-i tJ to (U n (U cn 1' ^O (U n) iJ 1 H 3 (U ij ij c iH in •o c 1 H tn tn o > h O X: rH -H (0 •rl XI 1 H (0 m •H 1 h 3 O PK (U (U O (U MH 0 a —1 g i-H ' ^ (0 1 o« U) » ' DQ (0 T) U 1 O c e x: E O X > o 0) W i« 1 o u x; O 0 0) S (u (U 1 H (U t-l e ' M •H ^ (U 4) •H U H (0 )-i (U 3 e (0 1 Z E -H (H M C 01 a u O (U tn o •H 10 O 3 ^1 1 A O H 10 10 0 •' g13 •H o to x: c ii £ to ! 3 O s J< £ Q 1 W Q CQ O C5 e ' osH^KqwD^w > 249 strongly related to domestic refuse and brick bhattas as the main items of degrading land quality recorded positive values of 0.99670 and 0.91522 respectively.

The second step analysis reveals the impact of garbage remains on the streets for a long time degrading land quality with a share of 0.98419 and brick bhatta recording factor loading of 0.40294. Factor II explained 40.00 per cent of the total variance explained. Factor III accounts for 11.38 per cent of the total variance and highlights the role of domestic refuse in degrading land quality of Baraut with loading of (+0.76166).

Quality of life

Factor I explains 56.14 per cent of the total variance and it points to various items that affects quality of life in Baraut. Migration (+0.98679), low income group people (+0.87940), lack of health facilities (+0.87940), shortage of electricity

(+0.78904) and unemployment (+0.67511) are the major contributors of the first factor. Factor II with variance of 32.10 per cent highlights the role of shortage of water supply (+0.90643), lack of health facilities (+0.47609) and shortage of electricity 250 (+0.47096) in degrading quality of life in Baraut .

Factor III accounts for 11.76 per cent of the total variance explained. It recorded high positive loadings of shortage of water supply (+0.63419) followed by absence of suitable schools that recorded positive loading of (0.34198). (Table-LXV).

Air pollution

Factor I of air pollution is strongly related to waste disposal (0.98769) and vehicles (0.96817) as the major contributing items of spreading air pollution in

Baraut. It explains 53.22 per cent of the total variance explained. It will be clear from Table-LXVI that quality of air of this region is greatly affected by vehicular traffic and wood burning with positive loadings of 0.94384 and 0.63918 respectively. Factor II accounts for 26.78 per cent of the total variance. The third step analysis highlights the role of waste disposal 0.43980 in degrading air quality of Baraut with a variance share of 20.00 per cent.

Water pollution

Factor I of water pollution explains 56.26 per cent of the total variance and it is strongly related 0) 1 251 Di 1 C 1 o •<)< •;j< 1-1 ^ O rH (TV in •H 1 CO CTi CO •<3< CO 00 CS O (j\ a^ T) 1 as iH •

1 H 1 H 1 H

'i ta 1 O 1 H 1 O 1 < (0 CO m 1 h W 1 Ul Ul rH c Ul 4J (U 1 O iJ ID VJ •H .-< 1 e w cn u XI 1 a-H v< c -H 4J (51 Id ID 1 Ul C ID U c d o 0) •H 1 •H D rH 3 ID 3: rH u •a u U 1 D XI ID Id ID n (0 1 U >. OJ u m (U 4-1 U JJ OJ a > 1 tn ID 43 10 -rH to iJ 01 >w a ro £ m O ID lO in rs 1-1 •rl 2 OJ > U Q 2 2 3 10 d 1 — - — + o u O 1 Ul 1 •"J* CO CPi CO r- tN M rN) r-l -H en 1 00 r^ o 'T 00 o LD o a\ •U C 1 n cr\ o o\ CJ^ ^ o o n •H 1 m rH <-l o o CO 00 •«< "O 1 c^n u> ••a* n 1 rH 3 •n rH 3 10 u 9lO) dxi ID -H u 4-1 (U U 3 m 5 2 2 Q H J 1 . +

CQ 1 cn 1 (n t~ "K" cn a^ t~ ^ o C 1 u} rH (N Tf n a^ 00 00 as 00 rH o m S ! o o o o o o o O o o o o + + + I I + + + + + 1 0, — + u •H

0) u C •H

a 0) 01 1 10 C 1 H 0) 1 a 0 ti -H rH 1 m 0 10 1 M •oH •^ m rH •9 1 Qi •P CQ r-l 4J 01 1 M •H 1 X 3 10 3 u s* 1 XJ U 1 (U r-l q (u rH 1 (U 0 u n) 0 •H 0) 0( § Ol U •(sU u CJ u » •rH Q.4J C V4 •ruH 0) >1 O ll-l 01 01 c ITl 4J 4J VH m <4-l 03 3 IQ •H « •H *> Ck m •H •H (0 3 Tl 10 Id 0) (0 lO o u n c 10 3: cn 2 a 55 EH •J M > 252 to septic tanks/ soak, pits dairy animals and waste water from houses with positive factor loadings of

0.92827, 0.86359 and 0.81425 respectively. Factor II accounts for 33.74 per cent of the total variance explained and is positively related to water logging

(0.90987) and waste water from houses (0.50402) in polluting water of the surrounding region. The third step analysis highlights the role of dairy animals, waste water and water logging in deteriorating water quality of Baraut with positive loadings of 0.66984,

0.41980 and 0.40091 respectively. Factor III explains

20.00 per cent of the total variance explained.

Noise pollution

It will be seen from Table LXVI that the Factor I of noise pollution accounts for half of the total variance. Vehicular traffic and loudspeakers are the main sources of noise in Baraut with positive loadings of 0.97639 and 0.89606 respectively. Factor II also registered traffic (0.98002) and loudspeakers (0.44392) with variance share of 32.14 per cent of the total variance explained. The third step analysis also highlights the role of loudspeakers in increasing noise with loading of 0.64199. This factor accounts for 17.56 253 per cent of the total variance.

Pollution related diseases

Environmental pollution through various sources leads to several related diseases that affects health of the people. Table-LXVII shows that air pollution in

Baraut results in several diseases. Factor I accounts for 47.36 per cent of the total variance and is strongly related to headache (0.99071), asthma

(0.97841) and nausea (0.94825) in degrading health of the people residing here. Factor II is strongly related to skin diseases, eye-irritation and bronchitis recorded positive loadings of 0.94825, 0.83607 and

0.78999 respectively. Factor III highlights the role of headache (0.41091) as the main disease that are affecting health of the people with a variance share of

20.00 per cent.

Water pollution of this region also results in various water-related diseases in Baraut. Factor I accounts for 65.01 per cent of the total variance and is strongly related to cholera (0.80789), jaundice

(0.75765) and diarrhoea (0.62250) as the main water borne diseases. Factor Ii hightlights dysentry as the TABLE-LXVII 254

Pollution related diseases in Baraut

Factor Diseases Loading Variance explained in %

Air-borne diseases

47.36 Headache +0.99071 Asthma +0.97841 Nausea +0.94825 Eye-irritation -0.54863 II 32.64 Skin diseases +0.94825 Eye-irritation +0.83607 Bronchites +0.78999 Headache -0.13599 Other diseases -0.12410 III 20.00 Headache +0.41091 Nausea +0.10248 Other diseases +0.10091 Asthma -0.41095

Total variance explained 100.00

Water-borne diseases

65.01 Cholera +0.80789 Diarehoea +0.75765 Jaundice +0.62250 Throat infection -0.38227 II 28.82 Dysentry +0.98067 Kidney stones +0.28060 Typhoid -0.93945 Diarrhoea -0.56364 III 6.17 Kidneystones +0.91401 Jaundice +0.77308 Cholera +0.57908 Throat infection -0.74241

Total variance explained 100.00 255 main water borne disease with loading of 0.98067. This factor explains 28.82 per cent of the total variance.

The third factor is strongly related to kidney stones

(0.91401) and jaundice (0.77308) with a variance share of 6.17 per cent.

Svunmary

The habitat quality of Baraut is not clean owing to the presence of garbage spread over crowding and fumes/ smoke. Air of the town is polluted from vehicles and waste disposal. Waste water from houses and water logging affect the quality of water in this region.

Vehicles and loudspeakers are the main sources of noise pollution which often leads to irritability and headache. Domestic refuse is responsible for degrading the land quality while presence of low income group people, shortage of water supply and lack of health facilities badly affect quality of life in Baraut. The water and air pollution of Baraut leads to several diseases related to pollution like headache, asthma, skin diseases, cholera, diarrhoea, dysentry and kidneystones.

9.4 SAROHANA

Sardhana, a tehsil headquarter lies at latitudes 256

28°8' North and longitudes ll^ll' East. It is situated about 21 kilometers away from Meerut with which is is connected by a metalled road. Other roads join to

Daurala in the east, Baghpat in the south-west, Baraut in the west and Shamli (in district Muzaffarnagar) in the north west. The total population of Sardhana in

1991 was 42969 with 22490 males and 20479 females. The handloom industry of this region enjoys a local reputation.

Hedsitat quality

Factor I explains 56.72 per cent of the total variance explained. It is strongly related to garbage spread (0.94630), drains flooding (0.92378) and foul smell (0.43845) in degrading habitat quality of

Sardhana. Factor II accounts for 28.15 per cent of the total variance. It highlights the role of foul smell, garbage spread and drians flooding with positive loading of 0.88121, 0.32308 and 0.31004 respectively

Factor III accounts for 15.13 per cent of the total variance and is strongly related to drains flooding with positive share of 0.98840. (Table-LXVIIl). 257

CO o t^ CO in 00 tN 00 rH in o o in rH 00 00 CTl 00 <-( m o o o •H 00 O in r~ 00 U3 O r- rH 00 1X1 tn d 00 T)

01 u H •H tn ID H c 0) f-H x; 0 ain E 4J o N (Hi 0) x: C 01 i-< O U e tn c u 0) rH a o 0) O tn 1-1 0a a 3a U 4J o <4-l 01 4) tn tn 01 (-H t-i a •a T) (0 XI o iH m 01 ID a 01 01 a i-1 (U 4J 4-1 ^ 3 4J U tn u •s •H u 0 CO c —I •4-1 Ol tn 4-1 r-i 01 a o yi 4-1 ^ . •H O 0) 0 XI XI (u •H OJ U ID 01 0 4J 01-rl CO u lO Ol 4J 01 to 4-1 U rH to n u •H •cH Id M Ol"^ >i •H XI flJ M (0 O O (0 •H -rl 4J 0 0 x: -H d 10 M S cQ CD e Q O (J Q to < 3 u J w s •H W (0 D Q O fc

M tH CO •sj" cr\ •* t~- tN in u> tn ^ CN CM rH C-- cn (N o o r- IXl CN •>J* in c~ cn ko o^ in rH m c rH n o iH 00 4J 10 01 O >H H H i •H x: C >.rH H & H C 01 E 4J U 01 4-1 a •H U o •H to a •H a OS c u •-< 0 U 3 o o >4-l • •H 0) •H to Ol U rH MH V4 I H ID X3 4J U O 10 •o o o XI 0) 01 M-l 10 U 01 u 01 4-1 4J M 01 *J •H 0) 4J •a c (0 o tn u • x: -H u rH 10 4J (0 -H 01 Ol 01 D OJ 4-1 D CO 01 3 nt cn XI -H a 01 XI 0) XI M 01 01 U U 0e) ^ 10 CO M )H E V4 tj to C 0 0 •O (0 ^^ -H 4-1 (0 (4 O 10 a-u c o x: x; fc O Q tn o U CD 3;§ D w w Id Q O u

CO o 00 in (N i-i m 00 crv o u> t^ in tN tN 01 ro t~- •M< U> O CN Tj" rH rH r~ O Tf •r» c 1X> ro 00 rH in CO CD ro O VO C~ in VO in tn 1< tN m cn vD in tN cn ro CO in in o O Tl< r-4 •H Id o\ m •'f a\ cn t~- fS

Id N >. 0) C r-i •H u r-< 01 a c •H a a a •H U 0 3 •3 •H 0o) 0) to » TJ U arH < Dl-H U OJ to U 01 u l< Di tn tn Ol c c H CO 4-1 c u r-< tn CO c •H H (0 c 10 10 (0 H 4J 10 •H C O 0) OJ 4J ID M XJ •H rH A •H •H »J V4 U 01 0 01 tJ U •r( "9 ^ (0 3 k t4 V4 i^ o 01 » tn £ c 10 O u > (0 Wl (0 (0 (0 D x: -H O X3 U a o o ai: CO m O Q CK O > > OfWX ^ < tn u tn w > 258 Land degradation Factor I of land degradation explains about half of the total variance. Table LXVIII shows that it is strongly related to improper garbage collection even garbage remains for a week degrades land quality of

Sardhana as revealed by the positive loading of

(0.96561) followed by domestic refuse (0.75813) that also play positive role in degrading land condition.

Factor II explains 27.84 per cent variance with positive figures for garbage dumped on the streets

(0.90864) and garbage collected once a week (0.73927).

Factor III of land degradation accounts for 21.86 per cent of the total variance. It highlights brick bhattas

(0.93595), garbage collected twice a month (0.87588) and domestic refuse as the main items of land degradation in Sardhana.

Quality of life

Factor I explains 42.11 per cent of the total variance. Shortage of electricity, migration and low income group people are the main contributing items of degrading quality of life in Sardhana with positive loadings of 0.98640, 0.55716 and 0.25517 respectively.

Factor II highlights the role of lack of health 259 facilities and absence of suitable schools in degrading quality of life with a variance share of 34.61 per cent. Factor III accounts for 23.28 per cent of the total variance explained and is strongly associated to absence of suitable schools (0.67981), unemployment

(0.51375) and congestion/ lack of open space (0.28080) in degrading quality of life.

Air pollution

Factor I accounts for 58.00 per cent of the total variance explained. It is clear from the Table-LXIX that vehicles, coal burning and waste disposal are the main contributing items of degrading air quality in

Sardhana as revealed by their positive share of

0.94694, 0.81049 and 0.80089 respectively. Factor II is strongly related to vehicles (0.97703) and wood burning

(0.91938) with a variance share of 31.03 per cent.

Factor III accounts for 11.00 per cent of the total variance explained and highlight the role of coal burning, waste disposal and wood burning in spreading air pollution in Sardhana.

Water pollution

Factor I accounts 60.00 per cent variance and is M o •>3< «3< tN CO U) ID o r- 00 01 tn en O O 1-H in 00 00 in (n i-f in VD CN in •Xl rH ^(N T ro •H U1 in n in [~- 1—1 as (N T) cn n 03 o o o o o o o o o o O + c + + 1 •J + + '

OS o H a 01 c (0 •H o c CO rt) u Dl\ 01 CO 01 3 C m M CO U a m •H a-Hc XI Oi C tu 0) c en c Ol (0 >i <-t -a O u (0 XI 3 -d 3 o 01 XI -uH u •H IW aCO ^^ T3 -a U-l •a 01 rt) O (0 •H ai rtJ 3 > o -l >i-H CO CO M > •H •n i-( iJ W 0) W 4J -a 3 A o 10 lO CO 4-1 •r^ Q 3 T3 a> o o a (0 (0 (0 S a 03 3 3 a c/] ^3 M

d CO ^ CTl j o o o (N f- o tn o o in in CTv > • 00 00 en

PI

U CO •rt 4J c •H

a T3 OS O 01 i r-( J.; (U fl U c (0 c 01-H iH 10 •H 3 T) O m • r\ (U fH i-H u3 TJ o c 0.9J M rH o u 0 3 J3 (0 ^ i-( (0 Q,iJ c Oi U < > O S 03 Q ^ CO 3 3 Q § 5 H > 261

strongly highlights the role of septic tanks and waste

water from houses in increasing water pollution of

Sardhana as revealed, by their respective loadings of

0.80902 and 0.75740. The second step analysis is

positively associated to waste water from houses

(0.56657), Water logging (0.54542) and dairy animals in

polluting water of the surrounding areas. Factor III

explains 8.00 per cent of the total variance and is

positively related to dairy animals (0.91578) and waste

from houses (0.32456) in polluting water of Sardhana

(Table-LXIX).

Noise pollution

In the first step analysis, loudspeakers used at

various functions are the major source of noise in

Sardhana with a loading of (0.94322). This factor

explains 71.77 per cent of the total variance. Factor

II reveals loudspeakers and industries as the main

sources of noise in Sardhana as they recorded positive

factor values of 0.97440 and 0.52731 respectively.

Factor III explains 13.00 per cent of the total variance. Vehicular traffic and loudspeakers are the main sources of noise in Sardhana with positive loadings of 0.96857 and 0.24098 respectively. 262 Pollution related diseases

Environmental pollution of this region leads to several related diseases which affects health of the people residing here. Table LXX shows that air pollution of this region results in various related diseases. Factor I of air borne diseases explains 53.16 per cent of the total variance explained and is strongly related to headache (0.98361), bronchitis

(0.87004) and asthma (0.70913) as the main air borne diseases. Factor II accounts 37.43 per cent of the total variance. Nausea and skin diseases are the main air borne diseases recording positive loadings of

0.93239 and 0.68014 respectively. In the third factor, headache is the main disease recording positive loading of 0.90244. This Factor explains 9.41 per cent of the total variance.

It is clear from Table-LXX that water pollution of

Sardhana leads to various water borne diseases. Factor

I explains 65.01 per cent of the total variance explained. It highlights cholera (0.80789), diarrhoea

(0.75765) and jaundice (0.64318) as the main diseases that are degrading health of the people. Factor II TABLE LXX 263

Pollution related diseases in Sardhana

Factor Diseases Loading Variance explained in %

Air-borne diseases I 53.16 Headache +0.98361 Bronchitis +0.87004 Asthma +0.70913 Skin diseases -0.73199 II 37.43 Nausea +0.93239 Skin diseases +0.68014 Eye-irritation +0.35732 Other diseases +0.21004 III 9.14 Headache +0.90244 Bronchitis -0.49009 Nausea -0.31246 Other diseases -0.21967

Total variance explained 100.00

Water-borne diseases I 65.01 Cholera +0.80789 Diarrhoea +0.75765 Jaundice +0.64318 Other diseases +0.21465 II 28.82 Dysentry +0.98067 Diarrhoea +0.93945 Typhoid -0.56364 Throat infection -0.55018 III 6.17 Kidneystones +0.91411 Jaundice +0.77308 Cholera +0.57098 Throat infection -0.74241 Typhoid -0.32920

Total variance explained 100.00 264 hightlights the major share of dysentry and diarrhoea in deteriorating quality of health with a variance of

28.82 per cent. Factor III accounts 6.17 per cent of the total variance. Kidneystones and jaundice are the main diseases recording positive loadings of 0.91411 and 0.77308 respectively.

Summary

The general conditions of environment in sardhana as revealed by factor analysis of various components is not clean. It is affected by the presence of garbage spreads, existence of foul smell and drains-flooding are common in the town. Vehicles, coal burning, wood burning and waste disposal are the main sources of air pollution which in turn leads to various disorders like headache, nausea, asthma and bronchitis amongst the residents. Rain water, waste water from houses and dairy animals create water pollution which again affect the health of people as diarrhoea, cholera and typhoid and other diseases are common here. Traffic and loudspeakers are the major sources of noise in Sardhana and causes irritation and headache. Domestic refuse, industrial refuse, garbage though collected once a week or twice a month degrading land quality. Shortage of 265

electricity, lack of health facilities and absence of

suitable schools are together damaging the quality of

life in Sardhana.

9.5 BA6HPAT

Baghpat, a tehsil headquarter lies at latitudes

28°57' North and longitudes 77° 13' East on the left

bank of the Yamuna about 50 kms. west of Meerut with

which it is connected by a metalled road. Baghpat had a

population of 24918 in 1991 with a growth rate of 45.24

per cent between 1981-1991. Previously, Baghpat was the

principal sugar mart of the district but Meerut city

and Tatiri with their railway facilities deprived its

importance. There after, opening of a sugar factory in

1956 helped in to regain its place on the industrial map of the district. Shoe making and iron-wares are the

other items of trade in Baghpat.

HeUsitat quality

Factor I accounts for 46.07 per cent of the total variance. In this factor general conditions of the environment is not clean due to the foul smell and drains flooding recording positive loadings of 0.98444 and 0.88915 respectively. In the second step analysis 268

over crowding, fumes/ smoke and drains flooding

recording positive factor loadings of 0.99954, 0.76055

and 0.45762 respectively. Factor II explains 31.13 per

cent of the total variance explained. The third factor

highlights the role of drains-flooding, fumes/smoke and

garbage spread with a variance share of 22.80 per cent.

Table-LXXI shows the factor loadings of habitat-

quality, land degradation and quality of life in

Baghpat.

Land degradation

Factor I explains 45.78 per cent of the total

variance explained. It is strongly related to domestic

refuse (0.98641), brick bhattas (0.95489) and garbage

remain for a long period on the street (0.99949) are

the main contributing items of land degradation in

Baghpat. Factor II highlights improper garbage

collection, domestic refuse and industrial refuse as main items of degrading land quality with a variance

share of 32.29 per cent. Factor III explains 21.93 per

cent of the total variance explained. This factor is positively related to domestic refuse (0.61984), brick bhattas (0.41084) and garbage collected once a week

(0.21973) in degrading land quality of Baghpat. (Table- 267

en m iH >JD •5J' fN (N CO Cr» LTI cn 00 •>3< CN CTv 00 CO r-i CO r~- '<:?' rH a^ C o cn cr\ a> r^ o OJ ^i^ cTi in n r-l iH rH (^ 1 PO rH .-I C> CO i-f n ^ fN rH rH W ^ fN rH 1 cn 'C ro f-H T}« m o o o o o o O o o 1 tH o o o o o I \ CN + + + 1 1-

Ai H 1> H OJ 3 0) x: tn O Id u OJ O •H 0) >.x: O (U c iJ rH JJ tJ H u *H a-H to O c •H rH o u < 0 •H D -H OJ 1) o Ci t-l rH cn m 4-J XI 0) XIdI "+-1 Q, U Id 0) 4-1 u 3 CJ 4-1 c •a w U fO x: O r-l --1 4J (0 0) cn 4-> iH OJ 3 Id X3 tt) e •H XJ 01 Id M-l U Dl OJ 0 m (0 M -^ cn to iJ 01 cn o C Id U M •H C to (D w >; Id C) c •H iJ C D, • H 4) U 3 (d o o u Id •H >H Id o x: ^ c P li. Q m o Q T3 J J CO < D

O) •"J" in fN U3 U3 rr o in t^ o ro ^ U3 o Oi in in U> iH o •o- •<»• (N en cn rH ^ (N t^ C CTNo [^ o in in CO r- ro 00 m ro O m •H ON vo in a\ Ol t- \s> (N cn cn tn CO rH rO O o T) CTl r- "a< , 01 H r> rH -H 0) •d M 0) Ol 4-1 rH (4 u c Q,-H a Id OS c -H 1 3 rH o 0) to -rl o 0 M-l OJ I E-i cn U a a 1) Id U Id o a) tn X) OJ l+H a Dl jj 3 iH (1) 4J 4-1 3 -rl C T) U M-l Id tn t). Id x: o 4J 3 4-1 cn •H nj a) 0) cn 3 0) in m CO Tl (U r-l V4 HH rH rH 4J cn •o 0) c O V4 i-i tw 0) rH >W (d t: •o o r-l o 0 O OJ 0) OJ Id 0 a Id C r-l CO u x: 6 M r-H -H rH O u OJ o ••-I () o tt) Id •H 0) DTtH 1,• H u 0) ^^ n u to 4J cn iJ Id O t-i 4-1 -u c •d C Id (0 cn o to Id U) 4-1 D- Id •H •H ja XJ 3 a 0) XI tt) iH M P. U 0) (0 l-( u to 1= u O U OJ D 3 > -n -rl u •H •0 M (0 Id c f1 m iJ x: (0 c o s Q O O M u D O to CO r^l D S J

CO 1< in o\ 00 H cn cn 'C 00 00 cn rf •* CN >1 rH cn •"J" H r-l IN ^ 00 •* CN ro ro 00 00 VD •u c >cl< a\ a\ U> •"J" cn O ^ cn CO rt> •o a\ CO vo cn cn cn cn (N c~ in o o o o o o o o O in o o o o o 1 1 + 1 1 in •J + + + + •f + + + J

to •U OJ td lU 0) -H CI (U C rH 4J •H •H u O c a •H C 3 c •H o 0) d) OJ •rt •3 O Dl T3 rH n. U T3 Id 01 XJ 10 OJ n o X lU T0l) ,Q C 10 a l«H C O a) u iJ U •rl H 4-> -1 -H H H i/i u t) Id (d h H n x: (d H 3 10 01 0) ni rH H 3 tH jj rH •< it-l 4-> r-t rH a iJ 01 Dl W rH tt 0) 4J r-t rH M-l X C CO X u Id o O o 4-1 1 0) h IC tl u (0 m •r1 SZ ' 10 () o H C 18 (0 o m o ^^ CO rJ z D <-i > Lxxi). 268

Quality of life Factor I explains 56.19 per cent of the total variance explained. Absence of suitable schools, presence of low income group people and migration are the main positively related items in degrading quality of life as revealed by their positive loadings of

0.99938, 0.91489 and 0.84784. In the second step analysis shortage of water supply, lack of health facilities and unemployment are the main items in degrading quality of life with positive values of

0.99890, 0.88313 and 0.81344 respectively. Factor II accounts for 23.10 per cent of the total variance.

Factor III highlights lack of health facilities, low income group people and shortage of electricity in damaging quality of life with positive loadings of

0.41982, 0.31972 and 0.19748 respectively. Factor III explains 21.71 per cent of the total variance explained.

Air pollution

Factor I of air pollution is strongly related to coal burning and vehicles as major sources of spreading 269

air pollution in Baghpat with a variance share of 46.05

per cent. Table-LXXII shows that Factor II is

positively related to waste disposal (0.99786),

vehicles (0.83115) and dead body burning (0.97250) in

deteriorating air quality with a variance of 28.80 per

cent. Factor III accounts for 25.15 per cent of the

total variance and it reveals the impact of waste

disposal (0.56917) and vehicles (0.31549) in spreading

air pollution in Baghpat.

Water pollution

Factor I accounts for 53.16 per cent of the total

variance and is strongly related to waste water

(0.99313) and septic tanks (0.95385) in deteriorating

water quality of this region. Factor II explains 26.07

per cent of the total variance and highlights the role

of water logging and waste water in spreading water

pollution as revealed by their respective loadings of

0.99735 and 0.25768 respectively. The third step

analysis is strongly related to water logging (0.64198)

and waste water from houses (0.50041) in degrading quality of life in Baghpat with a variance share of

20.77 per cent. en t~- ON O CM 00 rH 00 CO CM 27d Di W ^ tN CTi CTl rH cri •^i C a\ LTl U3 UJ iH 0^ o\ r-l a\ •H 113 rH tH H 0 "J" •* TH r- n in ro ^ CM U^3 in CM VX) ro (0 o 0000 0 t_3 0 0 0 + + I 1 + + ' + +

H H

g cn ij a

u «3 •H o 01 i-H 14-1 cn cn M 05 01 tn i-i C iJ c ^4 4J w O 4J Dl QJ C OJ a 01 4-1 (0 M (d i-H no O (0 oJ (0 jQ U OJ 5* (0 3 u •H a O) •H (U U ki OJ -r-l M-l 01 «d JJ -H 01 •J-l "D 03 x: - 01 a (0 3 0) > (0 (U (0 (0 S 3: CO H fJ •rl

a 01 U) tn 0 0 Ul 00 0 a\ (r\ o 00 iH in <-l ro U5 ro 1X1 CTl c r~ iH CN 0 c~ [^ 0 iH 0 o^ no t~ 'if cr\ in 0 0 •H CT\ 03 u> r~ CJ\ CM ro n•^ CM (0 0 0 0 0 0 0 0 0 0 1 1 o o + + + + + ' +

0) to -H o H a H H H x> Id H a I U cn H •H C a -H 1:1 o i-i u-i C o •H (0 (0 u 01 10 w 3 m 01 •^ m 9 0 u^ ja 4J C 0) (U a •H "^ U M D] u >,C (U 01 XI •H S > 0 oQ 3 s cn Id

d CO t~ (n cr> 0 0 ro in CTl CM iH cn o r- 1-1 H r-( in ^^ n r~ d a\ a\ (T\ r- cr> cr» r-- cn l, 0 (0 JJ 0 <0 0 (0 •H u JJ fl) » >M "O 3 •H (0 x: M (0 •1-1 u 0] a JJ u •H CO 3 "O > 0 Hi 41 m u (d « Q > & s cn 3 > a H •J M > 271 Noise pollution

Factor I of noise pollution explains 43.81 per cent of the total variance and highlights the role of vehicular traffic and loudspeakers as the main sources of noise in Baghpat with positive loadings of 0.98092 and 0.93891 respectively. Factor II recorded 22.04 per cent of the total variance explained and it reveals the impact of loudspeakers (0.34169) in increasing noise.

The third step analysis highlights the role of vehicular traffic (0.64198) and loudspeakers (0.31942) as the major sources of noise in Baghpat. Factor III accounts for 21.77 per cent of the total variance.

(Table-LXXII).

Pollution related diseases

Environmental pollution of Baghpat through various sources leads to various related diseases that are degrading health of the people. Air pollution results in several air borne diseases in Baghpat. Factor I is strongly related to headache (0.99351), eye-irritation

(0.96276) and asthma (0.93297) as the main air related diseases in Baghpat. Factor I explains about half of the total variance. Factor II with a variance share of

30.00 per cent reveals the impact of air pollution in 272 TABLE-LXXIII

Pollution related diseases in Baghpat

Factor Diseases Loadings Variance explained in %

Air-borne diseases J. 50.12 Headache +0.99351 Eye-irritation +0.96276 Asthma +0.93297 Bronchitis +0.72992 Skin diseases +0.59841 II 30.00 Nausea +0.91729 Skin diseases +0.80119 Bronchitis +0.68353 Other diseases -0.99957 III 19.88 Eye-irritation +0.61943 Headache +0.31982 Skin diseases +0.12543 Nausea -0.41988

Total variance explained 100.00

Water-borne diseases I 53.13 Dysentry +0.99313 Diarrhoea +0.96623 Other diseases +0.76971 II 23.74 Throat infection +0.99735 Diarrhoea +0.97762 Typhoid -0.53290 Cholera -0.30030 III 23.13 Diarrhoea +0.69753 Typhoid +0.41972 Jaundice +0.12473 Other diseases +0.11009

Total variance explained 100.00 273 the form of nausea (0.91729), skin diseases (0.80119) and bronchitis (0.68353). Factor III of air borne diseases is strongly related to eye-irritation

(0.61943), headache (0.31982) and skin diseases

(0.12543) as the main diseases that are degrading health of the people with a variance share of 19.88 per cent as given in Table-LXXIII.

Water pollution of Baghpat results in various water related diseases. Factor I accounts 53.13 per cent of the total variance highlights dysentry

(0.99313) and diarrhoea (0.96623) as the main water related diseases of this region. Factor II highlights throat infection and diarrhoea as the main water related diseases of Baghpat with positive loadings of

0.99735 and 0.97762 respectively. Factor II explains

23.74 per cent of the total variance. The third step analysis reveals diarrhoea, typhoid and jaundice recording positive values of 0.69753 and 0.41972 respectively. Factor III explains 23.13 per cent of the total variance.

Summary In Baghpat the habitat quality is affected by the 274 presence of drains flooding and fumes/ smoke. Vehicles together with coal burning and waste disposal pollute the air. Waste water from houses and water logging results in various diseases relating to water pollution- Traffic and loudspeakers are the main sources of noise pollution and causes headache and irritability amongst the residents. Domestic refuse and brick bhattas are damaging land quality. Absence of suitable schools, lack of health facilities and shortage of water supply are degrading quality of life in Baghpat. Headache, nausea and eye-irritation are the main air related diseases prevalent in Baghpat while dysentry, diarrhoea and throat infection are the major water related diseases that affect the health of the people residing in Baghpat.

9.6 KHARKHAUDA

Kharkhauda, a town area, lies at 28°50'North latitudes and 77°45' East longitudes. It is located about 18 kilometers to the south of Meerut Hapur road.

Kharkhauda had a population of 10549 in 1991 with a growth rate of 21.14 per cent during 1981-1991. The main industry of this region is manufacturing of agricultural implements which finds local market in the 275 town itself.

Habitat quality

Factor I of habitat quality recorded an unclean environmental conditions in Kharkhauda owing to the problem of foul smell (0.99965) and garbage in heaps

(0.94139) explaining a variance of 50.04 per cent.

Factor II reveals the impact of drains-flooding, foul

smell and garbage spread in deteriorating habitat

conditions with positive loadings of 0.99371, 0.71597 and 0.29460 respectively explaining a variance share of

29.96 per cent. Factor III is strongly related to garbage in heaps (0.71940) and drains flooding

(0.64518) and accounts for a variance share of 20.00 per cent. The factor loadings of each factor are shown

in Table-LXXIV.

Land degradation

It may be seen from Table-LXXIV that improper garbage collection and domestic refuse are the main

items of land degradation in Kharkhauda as revealed by their positive share of 0.98445 and 0.92295 respectively. Factor I which explained about half of the total variance. In few areas garbage is not tn 00 tXI r-n cn r-^ J*s 00 CO 276 o ro > O J^ C (J\ LO (J\ J> O cn VT -" -^ r-' o •H r-i iH 1X1 l-l rH in J- >;• rH ^ U3 U) CD -S" I— ^ o •a r~ n o O o o O O o o o o o o o + + + 1

n iH D tn o E s o 0) -. r^ x: u E 33 4J a u o -H di tn EH •H O O U 3 ^-1 -J rH D J-l •H tn OJ U M •a T3 ID VH XI in 01 I4H m (tj a 0) tt> 4-> 4-! U 4J lO C tn u U x; n) (1) -H D (1) 0) 4J •a x: T) C 4-1 rH (0 iH u ;j o •H 0) r-1 0) ID KH n> COM T3 U O iJ O rH Q) 0 •H rH I-H 3 u ID U M i-H UH . XI u IH 01 0) O 01 w cn uu J3 OJ U 0 ID tJ rH •H 0) •H OI 4J C Oi ID C It3 i—t 1-1 XI 4-1 OI U XI >H 0) E (0 d (u tn ID x: •H u 0 cn (1) U (0 0) XI -U (0 VH u ID x; jQ c > fc o E VH C CQ CO U •J cn ^ D O Q o 10 o •H

(U en iH r- o CN •J" 00 U3 rH r- o o 00 IM Oi ro a" •H c t^ in •S< 00 00 m 'J" U> TT O tN i-H -H t^ cn [^ CO cn tn o CO tn -a CTl c^ CN ITi M IT) O o o o O O o o o o o o o o o + + + ' + + + + + + I >i 4J •r4 iH cn t-\ x: c O nS 3 tn E O G > & u C E U U I H • H O -H tn a •d Pii 3 o (H U o O JJ d •rl 0) 0) H 10 3 e n a-H O tn '^ § H 4J O ID ••H U O C •O VH O O e Q CO u Q Dti (0 d Q O u m CO

in cn Ofl rv) in in IN Ts< in 00 m rH in VO n rH tn rH rH tn rO o cri rH ro in 'J' CN [^ CN CN in n o •H I cri •«f CJ> in 00 rM <-l CN tn in in t^ in cn cn cn tn , 4) Id rH -H 4) 4J a 4J •H a-H 3 -H tn -H •3 u T3 IH ID XI o cn CI M u o 01 tn u XI «< cn 01 U Di ID O C rH C) rH c (0 H ffl ID JJ o ID •H H rH .Q Wi XJ U yL a c o •H l-l CQ D Ij (U ^1 O U (u tn x: u ID «c O <0 > ID £ 10 u 10 > to ci< C3 O O CO J > tn 277

collected regularly and remains on the street twice a

month thus degrading land quality of the surrounding

areas with positive loading of 0.21764. Factor II

explains 26.68 per cent of the total variance

explained. The highest positive loadings is shown by

garbage collected twice a month (0.99824), domestic

refuse (0.38491) and disposal of garbage on the streets

(0.53678) which play on equally effective role in

degrading land quality. Factor III accounts for 23.02

per cent of the total variance explained and highlights

the role of domestic refuse (0.81943), garbage

collected twice a month (0.41009) and brick bhatta

(0.13418) in deteriorating land conditions of

Kharkhauda.

Quality of life

Factor I explained about half of the total variance. It reveals the importance of three items like

shortage of water supply (0.99128), low income group people (0.95391) and lack of health facilities

(0.75515) in degrading quality of life in Kharkhauda.

The second step analysis highlights the role of

shortage of electricity, absence of suitable schools and low income group people which affect quality of 278 life in Kharkhauda and recorded positive shares of

0.99627, 0.89450 and 0.30010 respectively. Factor II accounts for 35.35 per cent of the total variance.

Factor III explains 14.00 per cent of the total variance explained and reveals the impacts of various items in degrading quality of life in Kharkhauda. The highest positive loadings in this factor is shown by lack of health facilities (0.56173), shortage of water supply (0.43109) and absence of suitable schools

(0.13198) (Table-LXXIV).

Air pollution

Factor I of air pollution recorded a variance share of 51.92 per cent. Table-LXXV shows that waste disposal (0.99932), wood burning (0.64968) and vehicular traffic (0.57040) are the main items in degrading air quality of Kharkhauda. Factor II accounts for 29.08 per cent of the total variance explained and is strongly related to vehicular traffic and wood burning with their positive share of 0.98179 and

0.76021 respectively. Factor III which explains 19.00 per cent of the total variance explain is positively loaded to waste disposal (0.81978), vehicular traffic CX3 o O 00 O) n CO -a" r~- 279 o o (71 CO 'a" cr. CO 171 c CT\:^ cr\ ro en ^ TH r-t rH •C rH r^l rH rr. LH . O • O ^ rH TJ* rH fNj n 00 U3 •^ • o O O O O o o o + + +

H H H

O H O <

r-1 M 00 <0 Dl 01 03 U C r~< 01 O iJ •rl iH 10 u CO CD 0) tt) 01 a •eH (1) OJ c 01 4.) M d) r—I fO ^1 0 fO C 10 'H XI rH 3 (0 U 0) tH A; (0 3 XI •H Q, JJ v< •H (1) U U D >, MH 01 01 i-l -H rH (0 0) O (0 10 lO )H O C s > u 3 S Q H r3 M

d 01 CP> rH U) [^ vu no fN rH fM 00 Dl r~ •sr u> ro IN in !N 00 OJ -a* rH o C rH «i< "T rH CTK r~r o ro c~ r~ "T •H •H 00 r- o (N CTl U3 O rH 00 -a" t^ 1 VD -a cr\ CTl CT\ 00 (n CT\ O) -a* (Ti r- ro 1 lO ;3 (0 o O o O o O O o o o o o 1 VO •J + + 1 1 + + + 1 + + 1 1 ro o PI •r4 T) iJ o SH JJ JJ D T3 ijH 3 U x: O (0 ^ •H Q< 01 "O 3 10 T3 0) 0) s u: a H nt »

CO (N 00 o ro VD ro c^ ) r- d en ro >J3 •<»• in fM r^ r- rH cr> Ol (N •* t- 00 rH M 01 •H JJ 0} 1 C •H JJ 1 -H

a c 1 -O 10 1 0) o M JJ 1 C a (0 3 ti 1 -H o 0 •-* 0 1 10 •H 01 01 rH •H 1 r-* bi 4i C 4J 01 1 a a -rl ^1 ^ o fl U 1 K CO H 01 » 3 3 (U C a EH r3 M 1 > 03 M 280 (0.61900) and coalburning (0.41900) in deteriorating air quality of Kharkhauda.

Water pollution

Factor I accounts for 49.83 per cent of the total variance explained (Table-LXXV). It is strongly related

to water logging (0.99926) and waste water from houses

(0.97913) as the main items of spreading water pollution in Kharkhauda. Factor II explains 30.16 per

cent of the total variance explained. The highest positive loadings are shown by dairy animals (0.99926),

septic tanks/ soak pits (0.96753) and waste water

(0.20322). Factor III highlights the role of water

logging, (0.64198), waste water (0.31988) and dairy animals (0.12943) in spreading water pollution in

Kharkhauda region with a variance share of 20.01 per cent.

Noise pollution

Factor I accounts for 46.34 per cent of the total variance explained. Table-LXXV shows that vehicular traffic and loudspeakers are the main sources of noise

in Kharkhauda as revealed by their positive loadings of

0.83798 and 0.15892. The second step analysis also registered loudspeakers (0.98709) and vehicular traffic 281 (0.74742) as the main items in generating noise with a variance share of 35.66 per cent. Factor III again registered traffic (0.41398) and loudspeakers (0.13984) as the main sources of increasing noise in Kharkhauda with a variance share of 17.00 per cent.

Pollution related diseases

In Kharkhauda, environmental degradation leads to the spread of various pollution related diseases. Air pollution of this area results in various diseases as given in Table -LXXVI. Factor I accounts for 43.69 per cent of the total variance explained. Eye-irritation

(0.84322) and skin diseases (0.67989) are the main diseases which affect the health of the people. Factor

II accounts for 30.00 per cent of the total variance and is strongly associated to nausea (0.99963), skin diseases (0.73332) and eye-irritation (0.53757). Factor

III explained 26.31 per cent of the total variance. It highlights headache (0.51980) and eye-irritation

(0.41063) as the main diseases that are degrading health of the people.

Water pollution of Kharkhauda results in various related diseases. Factor I of water borne diseases TABLE-LXXVI 282

Pollution related diseases in Kharkhauda

Factor Diseases Loading Variance explained in %

Air--boime diseases I 43.69 Eye-irritation +0.84322 Skin diseases +0.67989 Headache -0.98675 Nausea -0.61908 II 30.00 Nausea +0.99963 Skin diseases +0.73332 Eye-irritation +0.53757 Bronchitis -0.23590 Headache -0.16226 III 26.31 Headache +0.51980 Eye-irritation +0.41063 Nausea -0.13194 Bronchitis -0.43174

Total variance explained 100.00

Water--borne diseases I 50.90 Typhoid +0.99726 Throat infect;Lon+O.9972 6 Jaundice +0.90065 Diarrhoea +0.88574 Kidneystones -0.70541 II 26.10 Dysentry +0.99726 Cholera +0.98987 Diarrhoea +0.70880 Kidneystones -0.46418 III 23.00 Diarrhoea +0.51980 Cholera +0.41975 Jaundice +0.13499 Kidneystones -0.31977

Total variance explained 100.00 283 explained about half of the total variance and is strongly related to typhoid (0.99726), throat infection

(0.99726), jaundice (0.90065) and diarrhoea (0.88574).

Factor II highlights dysentry (0.99726), cholera

(0.98987) and diarrhoea (0.70880) and explained a variance share of 26.10 per cent. Factor III accounts for 23.00 per cent and is positively related to diarrhoea (0.51980), cholera (0.41975) and jaundice

(0.13499) as the main water related diseases that are damaging the health of the people residing in

Kharkhauda.

Sunnnary

The above discussion makes it clear that foul smell, garbage spread and drains-flooding are degrading habitat quality of Kharkhauda region. Waste disposal,

Vehicles and coal burning in few areas recorded positive factor scores as sources of air pollution.

They lead to several diseases relating to air pollution. Water logging along the problem of waste water from houses and dairy animals are polluting water and causing typhoid, dysentry, cholera and diarrhoea.

Loudspeakers along with heavy traffic contribute in spreading noise pollution which reflects in 284 irritability and headache among the local people.

Improper garbage collection and domestic refuse are degrading land quality while lack of health facilities, shortage of water supply and absence of suitable schools are deteriorating quality of life in

Kharkhauda.

9 .7 BABUGARH

Babugarh, a small town lies at latitudes 28"43'

North and longitudes 77°50' East on the Lucknow-Delhi road and about 8 kilometers from Hapur. Babugarh town area had a population of 3566 in 1991 with a growth rate of 49.27 per cent. Babugarh has not registered industrial establishments. It has only one millitary farm.

Hedsitat quality

Factor I of habitat quality recorded an unclean environmental conditions in Babugarh owing to the problem of fumes/smoke (0.99891), garbage in heaps

(0.93522) and over crowding (0.26627) with a variance share of 62.22 per cent. The second step analysis reveals the impact of garbage found in heaps, foul smell and over crowding in degrading habitat quality as 285 revealed by their positive loadings of 0.96390,

0.94108 and 0.35408 respectively. Factor II accounts

24.68 per cent of the total variance explained. Factor

III explains 13.10 per cent of the total variance is

positively related to fumes/ smoke (0.81311), garbage

in heaps (0.76413) and drains-flooding (0.13417)

(Table-LXXVII).

Land degradation

It is clearly observed from Table LXXVII that

factor I of land degradation is strongly related to

improper garbage collection, disposal of garbage on the

streets and brick bhattas as the main items in degrading land quality of Babugarh as revealed by their positive loadings of 0.99255, 0.98034 and 0.93423 respectively. Factor II explains 20.52 per cent of the total variance explained. Garbage remain on the streets or along the roadside for a week, domestic refuse and disposal of garbage on the streets are contributing their share in damaging quality of land of Babugarh as revealed by their positive loadings of 0.98740, 0.97203 and 0.51669 respectively. The third step analysis highlights the positive share of domestic refuse

(0.98835) and garbage collected once a week (0.81536) 286 rH m 'S* cn ro w tn VJ3 CO ro rH O •SI' o cn ro c n •q' "S" en in Lfl O rri [^ 0> O rH rH i-i U3 m on rH t^ O rH CO cn o ro ro <* o VD ^ rH T3 00 [^ >-» t (TV 00 00 CO 00 •-H CO > (d O o o o o o o O o o o o o + 1 1 t 1 1 1 + + + + + +

rH <0 01 a 0) •H •H rH >i 0) u c JJ QU jJ •rl a •rl u •rH 0 c C rH 3 U o 3 01 •H 03 •rl Dl U M •a e 10 01 (0 >H jJ 01 c 01 XI 01 IJH 01 U a 01 (U jj o 01 u 3 JJ 0) (0 C 01 tj T) i-> 10 UH x: 10 rH a 01 01 • rl tr 01 JJ 3 01 u x: -a m ^ a 01 u <-< JJ m o (1) •-I f= t-l (0 UH C 'JH c o 0 c o f-{ 0) 0 01 O w o x: C u •H rH •H 5i 01 (U 01 o rH tt) 1 •rl 01 01 JJ ra 03 ^1 MH Dl •H O 01 XI Ol 01 4-) oi>: 01 U 01 JJ JJ O 10 JJ r-^ (0 01 JJ 10 D, u na (d C W m 01 (0 0) o 01 XJ H ^1 ,-1 01 T) U 0 Ol 01 O •H :* U (0 O IT) (0 o •H JJ c (0 x; •H c x: -rl (0 El, O Q a

•H o 00 00 r-t o ro CTi t + + + ' + + + 1 CM rv) •H h 03 rH 0 W >, O 01 & >i--l 01 x: -rt H (1) c JJ a rH U JJ o o •H D. tt W -H c U 3 O r^ o 01 •H 01 0> 0) -H ^ 01 ^1 ttrH U >4 (d T) (0 01 JJ U XI <0 »:i m (U XI 01 U 01 ft 10 tH 1 d a m 01 u 3 01 JJ 3 ^ « u 01 to r-l (0 H ro c MH 0 •H x: o aj m •H 0) 3 Ol 01 01 3 M 3 -^ iJ •H (0 x: C "O- r-( HH Ol 01 rH 4J •H <*H <«H IJH () rH 01 JJ (0 9 Id CO C rH T) O O U o rH JJ O O 01 IH 01 H •0 (0 o u (0 o -H 4-1 c ^^ x: x: •H O XI 10 o tu ^ u u (0 Q u 01 M cu w w S J < •a s

01 rH CM t~- f*! in "^ ro t~ in cn rH ro ro C~ ro >t (T^ tS (N t^ in CM rH o eg CM o VD 00 m •u c 00 1/1 W) cn tN CTi Ol en CT> r~ cn ro o\ c~ U>

01 01 Id 01 1 oVP c rH >. 4J u c 01 •H 01 ft •IJ •H •H o u C 01 C 01 ft-H c 3 c 3 JJ -H a 3 U •r( 0) o •H o •H 0) 01 -n •3 01 e 0) •o IM U rH (H T3 « m •n 01 10 X3 ^ J-> 01 (U 41 o UH (0 0) O C &; a nc c c •H o 4J V4 JJ f1 •H D4 J o»o 01 tJ < 01 D M M > 287 in degrading land quality with variance of 19.18 per cent.

Quality of li£e Factor I of quality of life in Babugarh explains

60.19 per cent of the total variance explained. Table-

LXXVII shows that congestion/ lack of open space, lack of health facilities and absence of suitable schools are the main contributing items in degrading quality of life with strong positive loadings of 0.99929, 0 78521 and 0.65403 respectively. The second step analysis reveals the impacts of shortage of electricity and shortage of water supply in damaging quality of life with positive loadings of 0.42992 and 0.24099 respectively. The factor second explains 22.41 per cent of the total variance explained. Factor III accounts for 17.40 per cent of the total variance and is strongly related to lack of health facilities and shortage of water supply as the main items in degrading quality of life in Babugarh with positive figures of

0.89701 and 0.70943 respectively.

Air pollution

Factor I of air pollution recorded a variance 288 share of 71.05 per cent of the total variance. Table-

LXXVIII shows that vehicles (0.91384), coal burning

(0.88547) and waste disposal (0.78170) are the main items of degrading air quality of Babugarh. The second step analysis reveals the impact of vehicular traffic, waste disposal, kerosene burning and wood burning in degrading air quality of Babugarh as revealed by their positive loadings of 0.98853, 0.62366, 0.40608 and

0.38239 respectively. Factor II explains 18.25 per cent. The third factor of air pollution highlights the role of vehicular traffic and waste disposal with positive loadings of 0.95645 and 0.86710 respectively.

Factor III explains 10.70 per cent of the total variance explained.

Water pollution

Factor I of water pollution accounts for 70.14 per cent. This factor is strongly related to waste water, dairy animals and water logging in deteriorating quality of water as revealed by their positive loadings of 0.98764, 0.92180 and 0.88193 respectively. The second step analysis highlights the role of water logging, septic tanks/ soak pits as main items of spreading water pollution with positive loadings of en IX) O U) VO in r~ U5 o^ O CO rH Di •<}i rH [^ in rH r- lO LI V£) ^ O C 1J3 t^ in o rn ID o o vD O ro in vn m rH •3" »H rH 1 O cn •H o a> r- in 289 •j\ cn Tl 00 vo vr) 00 CO ir> • o cn CO 00 ni CO O o o o o <_) o o 1 ro o o o + + 1 I + 1 ft rH +

H H H

O to iJ C rO 01 4J c 3 •H r-H r-H C 1—t (0 H 0 tfl Oi tn 3 01 Ch<-< C to •H O XI C l-i (0 U r-H Qj -H 01 01 OJ 10 •eH M >, C u (0 01 J^ OJ u -H to -H T3 t-l (0 (0 -H 3 U c(0 r-ol OJ V^ 0) T! O 3 01 •rul -H XI XI u a^j 0) tfl ItH U 0) CO CO >. u M-l •H 4J T3 r-l u 3 OJ T) 3 tn T) •uH (0 3 -O £ tn (0 <0 u m (U (d (u o 10 C (0 (0 o c > s Q a 3 M Q 2 C~^* *J I—' a •H h a o w ro U) 00 CN CT\ •>j< c<-n( rH CM rH r^ 4J c 00 CN O CO a\ rn •<»< t-- O 01 00 H •H oi U) ^ ro H 01 (0 3 O 0 I M -cH to rH o (0 c Ol\ o CO u to u 01 c to Q,r-H to •H o 7i c •H Jd (0 u 4J CO axi •H 01 C rH E OJ to 0) tfl c DI ns (0 •H a 0) r-( -H •H C -H (mU Xl a) u r-ol u m rH XI c a 0) CO u •H to to MH ffl P4 •H iJ O X) OJ iJ 3 £r T3 •« -1 (0 x; CO M o 4-1 aT3 •H 3 (0 Tl M (1) (rt OJ 10 4) C (0 (1 V^ CI > i^ o M l-H 0) > S s s M Q ^ H 4J (d

d m •<5< [^ O O •51< O rn in 1 CM lO I" o Di 00 -a* r~ CO U} 00 1 i-< C^ Ol rH H •a ITJ o o o o O O o O 1 o O o o H + + + I + 1 r- 1 1 O o + + + +

a, <*• u to 1 c •H U 1 •H rt 1 0. 1 T3 0) M 1 C C (0 1 •H !Z 0 1 (0 o rH C O to 1 t-< o H !3 « w H to 01^ 1 a H U O 01 to 3 r-t c CO 1 X a H c o n & B u <0 M 1 X i-l 0) e O) d 1 iJ CO OJ 01 to H] iJ H (0 1 »J OJ j«; i/i •»-l •^ O III t; g' »J 1 <1) O -H (0 OJ ai 3 f) Oi 10 —1 P< U IH OJ U i f—1 'n u 3 o XI XI » U 1 •H 4J a c 0< u (U Hi 0) u H 1 H« 01 o 05 (11 (0 (0 <0 0) 1 (0 o u c o »< > O S Q !S< S Q S M 1 a H M J > <0 > 29Q

0.99946 and 0.73409 respectively. Factor II explains

16.80 per cent of the total variance explained. The third step analysis reveals the impact of waste water in increasing water pollution of Babugarh with positive loading of 0.94315. Factor III explains 13.06 per cent of the total variance explained (Table-LXXVIII).

Noise pollution

It may be seen from Table-LXXVIII that factor I is strongly highlight traffic as the only contributing source of noise pollution in Babugarh with positive loading of 0.78902. Factor I explains 56.91 per cent of the total variance. The second step analysis also registered traffic and loudspeakers in generating noise in Babugarh with positive loading 0.99209 and 0.98197 respectively. Factor III of noise pollution is strongly related to loudspeakers and traffic as the main sources of noise pollution as revealed by their loadings of

0.99660 and 0.87043 respectively.

Pollution related diseases

Environmental pollution leads to several pollution related diseases in Babugarh. Air pollution of this area results in various diseases as given in Table- 291

LXXIX. Factor I accounts for 64.55 per cent of the total variance explained. Eye-irritation (0.90391), nausea (0.80031) and headache (0.89920) are the main diseases that affect the health of the people. Factor

II accounts for 20.39 per cent of the total variance and is strongly related to asthma, bronchitis and headache as revealed by their loadings of 0.91942,

0.59959 and 0.43755 respectively. Factor III of air borne diseases hightlights eye-irritation, headache and nausea as the main diseases with positive share of

0.81649, 0.80548 and 0.74910 respectively.

Water pollution of Babugarh also leads several pollution related diseases that are affecting health of the people. Factor I is strongly related to dysentry

0.98611, cholera 0.96250 and diarrhoea 0.83989 as the main water related diseases of Babugarh which explains

46.27 per cent of the total variance. Table-LXXIX shows that Factor II reveals the impact of water pollution as water related diseases, throat infection 0.98727, typhoid 0.96919, diarrhoea 0.44828 and cholera 0.27127 are positively recorded in this factor with positive share of 33.13 per cent. Factor III of water related diseases points to diarrhoea and typhoid as main water TABLE-LXXIZ 292

Pollution related diseases in Bed>ugarh

Factor Diseases Loading Variance explained in %

Air-bome diseases I 64.55 Eye-irritation +0.90391 Nausea +0.80031 Headache +0.89920 Bronchitis -0.60031 Asthma -0.39329 II 20.39 Asthma +0.91942 Bronchitis +0.59959 Headache +0.43755 Skin-diseases -0.98281 Other diseases -0.95454 III 15.06 Eye-irritation +0.81649 Headache +0.80548 Nausea +0.74910 Asthma -0.84134

Total variance explained 100.00

Water-boxne diseases I 46.27 Dysentry +0.98611 Cholera +0.96250 Diarrhoea +0.83989 Kidneystones -0.99976 Jaundice -0.99265 II 33.13 Throat infection +0.98727 Typhoid +0.96919 Diarrhoea +0.44828 Cholera +0.27127 III 20.60 Diarrhoea +0.83919 Typhoid +0.74634 Cholera +0.64918 Other diseases -0.65946

Total variance explained 100.00 293 related diseases that are degrading health of people of

Babugarh with positive share of 0.83919 and 0.74634 respectively. Factor III explains 20.60 per cent of the total variance explained (Table LXXIX).

Summary

It becomes quite clear from the description of

Babugarh that garbage is present in heaps which makes general environmental conditions unclean. Air pollution is mainly due to vehicles and improper waste disposal while accumulating in various places leads to water pollution. Traffic is the only source of noise pollution. Domestic refuse is responsible for degrading the land. Shortage of electricity, lack of health facilities and absence of suitable schools are damaging quality of life at Babugarh. Diarrhoea and typhoid are the two important water borne diseases while headache and eye-irritation are the main air borne diseases of this region.

9.8 HAPUR

Hapur is a tehsil headquarter of district

Ghaziabad and the city has a status of Municipal board.

It is situated at a distance of 30 kilometers to the 294 south of Meerut on Meerut-Bulandshahr road and is located at 28°44' North latitudes and 11°^!' East longitudes. It is also connected by a national highway with Ghaziabad which is about 34 kilometers away. Hapur is also a railway junction for Delhi-Moradabad and Meerut Khurja railway lines. Chijja Nala and Kalinadi border the city and provide chief lines of drainage.

The municipal limit of Hapur city extends over 86.24 sq. kilometers and carry a population of 146591 persons in 1991 with 78464 males and 68127 females. Hapur is a leading grain and jaggery market of the country and is well known for its Papad.^ Brass utensils and handlooms clothes manufactured have enjoy local reputation. Hed^itat quality

The result of the environmental quality of Hapur recorded an unclean conditions of environmental (Table-

LXXX). Factor I is strongly related to garbage spread, drains-flooding and foul smell as revealed by their positive share of 0.98239, 0.50721 and 0.44731 respectively. Factor I accounts for 66.91 per cent of the total variance explained. The second step analysis

1. Papads are thin, oval, large, fried wafers 1

m >-l C^ U3 o> o vo o • (N n rH in vx> C-- (*! t~- 0•*0 c r- rH • H U> (*1 V tN r>i o 00 CO o ro 1 •a

HI H u H Id H a x: tn >, >. r^ C tu o £ i-i a (U •-^ o -H a a a u u U 3 o 0 l«H •H cn tu iH iw a •o XJ u 0 tn u (U a Dl 0) 3 0) 4-) M 3 C tn MH u rH Id u 0 U 3 (U (U s Id c -a iw M 0) rH 01 •H O HI IM IH in (H rH o O "c^ OJ a •o o --I Id o CJ •0H m r-l O "H (U 0 Si j-i e •H SH (U cn cn 4-1 u CJ CO Dl U 4J Dl JJ Id Id tn •H tn tn (1) •cH •H C (^ O o C Id 4J x: x: 0 0 0) Q M O tn CO CO CJ J •rt - 1

cn in m •'5' Cr\ rH in U3 00 00 ^ m Dl I* vo iH in in c~- •* o\ c~- CM •"I" O C tN in iH C^ CN 'j- CTl rH TJ- cn n •H \D CM (N \D O •'1' CTl o rH o r^ 1 > a\ n n [~- 1 (0 •* >i O o o O o o o o o o o o CN 1 4J 1 1 -H H3 + + + + + + + + ' n 1 H 1 Id (U C u & (0 cn Id •H rH a u o tn tn •d T3 o CI X OJ 'H r>-H . d C x; rH iJ (cU m •H u -H a X in a. D. Q, o rH o 3 Hi a o tu 01 (U -rl tn I H Dl tj I4H o Id <- (U (U O t-i a 01 u (U y. Dl M e 3 10 w e •rl cn s u c 0 d 3 O VJ -H O u o Id o -C b. Cb Q Q Q m ;§ J r^l U U)

•u cn *• n •H cn n (V n o C^ If in c~ o O fl 00 c (N C-- t^ (N •"l" T(< r-i 00 rH iH n cn c^ •H CO o i< CO 00 lO •^ rn CN in ID O 1 T) CTl in 'i' 00 cri CO in 'J' tn a\ c~- ro rH 1 nj (0 0 o o o o o o o o o o o O in 1 & •^5 + + + \ + + + + + + + + •f 1 •u fl) •u c OJ o\» 1 (U •H a a c i o o •H 1 (U IH a -O 1 o (0 V^ () (11 Id (d D-H C o Q4 0 Id 1 n C3 Q Ci, O > > OZ D u tn •J > 1 296 reveals the impact of fumes/ smoke (0.96254), foul smell (0.82563) and drains flooding (0.22114) in degrading habitat quality of Hapur explaining a variance of 22.64 per cent. Factor III explains a variance of 10.45 per cent highlights over crowding, drians flooding and foul smell in degrading habitat conditions with positive loadings of 0.96931, 0.83297 and 0.34386 respectively.

Land degradation

It is clearly observed from Table-LXXX that domestic refuse, disposal of garbage on the streets and irregular garbage collection are the main items in degrading land quality of Hapur in Factor I with variance share of 50.60 per cent. The second analysis highlights the role of domestic refuse and brick bhatta in damaging land quality of Hapur as revealed by their positive loadings of 0.50251 and 0.44475 respectively.

Factor II explains 37.39 per cent of the total variance explained. The Factor III with 12.10 per cent of variance is positively related to industries (0.92179) and domestic refuse (0.72530) as contributing items in deteriorating land conditions of Hapur. 297 Quality of life *"'' The result of factor analysis concerning quality of life are shown in Table-LXXX. Factor I accounts for 45.10 per cent of the total variance explained is positively correlated to migration, unemployment, congestion and low income group people in degrading life quality of Babugarh with their loadings of 0.99809, 0.92101, 0.75934 and 0.36783 respectively. Factor II accounts for 32.77 per cent of the total variance highlighting absence of suitable schools (0.99946) and low income group people (0.77198) in deteriorating quality of life. The third step analysis is positively correlated to shortage of electricity, shortage of water supply and congestion/ lack of open space with their loadings of 0.98760, 0.58734 and 0.50700 respectively. Factor III explains 22.13 per cent of the total variance explained. Air pollution

Factor I of air pollution explains 45.56 per cent of the total variance. It is strongly correlated to vehicles (0.93415) and coal burning (0.95594) in deteriorating air quality of Hapur. The second step analysis highlights waste disposal, vehicles and bhatta 298

units in damaging air of the surrounding region with

positive loadings of 0.95522, 0.89665 and 0.24253

respectively. Factor II accounts for 31.88 per cent of

the total variance explained. In the third factor

concerning air pollution, vehicles, kerosene burning

and waste disposal are the main items of spreading air

pollution in Hapur as revealed by their positive share

of 0.96983, 0.98937 and 0.66918 respectively explaining

a variance share of 22.56 per cent (Table-LXXXI).

Water pollution

The result of factor analysis in determining water

pollution of Hapur are shown in Table-LXXXI. It is

clearly observed that factor I of water pollution is

strongly related to waste water, septic tanks/ soak

pits in damaging water quality of Hapur as revealed by

their respective loadings of 0.93841 and 0.60798

explaining a variance share of 64.91 per cent. Factor

II accounts for 24.13 per cent of the total variance

and highlights the items of rain water producing water

logging and waste water from houses in polluting

environment with positive values of 0.93352 and 0.48761 respectively. The third step analysis also reveals the en m r~- 00 o tN C~- <" l^ (sC CT^ in r- cc m CD CO iH (N in ^ 00 c cTi 0^ o^ LD O 00 (N a\ CT^ O -H vo ^ *^ ro 00 VO t-( l£l ^^ O 299 n O^ CTt VD 00 o^ r- CTi in 1^ •-I (0 o o o o o o o o o o o -q + + + 1

H H H

O H U «: c (0

•cH ^H c (0 O en u Ul M a,r-H cn 3 O J-l (O 1-. XI a-H 0) m 0) OT C J^ SJ I—I CO QJ •H D (0 C ID •r-4 XI OJ C '0 ID u 0) U (0 r-l G •H a 4J U W c; miJ tn >. U-l OT -1 •-^ 0 4-1 iJ u 3 in T5 ;;2 ro x; i-i M (0 OT -a -^ !0 3 •;J > OJ d) to £ (D C (0 U (1 c > i^ S ffl S w Q H J

o •H (\ in PO t-l CN TH o (N •<}• m r^ cr\ CTi ro in (Ti 00 << l£> ro o H "^ in n m -a CTl 00 rg en a\ •cr H in r^ r^ CN H (0 O o o o o o o o O + + ' (U n •H O H ci X H XI -d H C/1 X a K O C I H fO H U i-i o 3 -H 9 +J ID Ol O 0 W 01 OT H 0) O c •cH a V-l H r-H a 01 to (0 4J tn "O 10 3 Tl x: o (0 <0 C S-l O t:; IT) OQ O S 3 M E-I K-l t-H

to in Tf n • r- CT^ U) u> CO T ro 1 i-H (0 o o o o o O 1 in H o O o o o 1 1 1 C^ 0 H3 + + ' + + ' + +

Q<

1 oV> M tn •H 4J tn 1 C •H 4J 1 -H a c (0 1 X) >; 4J 1 HI O (0 D 1 C E-i O rH SS ) -rH U cn i-i O 1 (0 »»: S •^ O H 1 r-1 o 01 tjl M tn a a in 1 a H ecu X B 1 X to •H -H -H C rH j 0) tn 1 (LI (U B C C C to (0 ij ^4 OJ I—I »J U1 U ^j 3 0) o m •H ' OJ X) i4 11 3 D 4-1 -H u 04 U (LI u 1 U (D O --1 13 XI 10 c •H Q, 4J 1 C •H Ot U u U U W 14-1 OT M 1 0 t-l •H •-t "D u •H tn M 14-1 •a 3 •rH (0 « x; (0 0 (0 u 3 H (0 3 T) Vj > H OJ 0 0 x: a-a (0 O ^4 O C 1 (tj rt; > U 2 CQ 0) C a H -J M • > CO M > 380 impact Of industries and waste water from houses in polluting water of the surrounding areas recorded positive loadings of 0.98052 and 0.76847 respectively.

Noise pollution

Factor I accounts for 75.13 per cent of the total variance explained. It is positively related to vehicular traffic and loudspeakers as the main sources of noise in Hapur as revealed by their loadings of

0.87374 and 0.42537 respectively. Factor II of noise pollution highlight the role of traffic in increasing noise pollution in Hapur with positive loading of

0.56956. Factor II explains a variance share of 19.21 per cent . The third factor with low per cent of variance 5.66 per cent also registered traffic as main source in generating noise in Hapur (Table LXXXI).

Pollution related diseases

Environmental pollution through various sources results in several pollution related diseases in this area that are degrading health of the people. Air pollution also results in various diseases as given in

Table LXXXII. Factor I of air-borne diseases is strongly related to asthma (0.97658), bronchitis

(0.86794), eye-irritation (0.76054) and nausea 301 TABLE-LXXXII Pollution related diseases in Hapur

Factor Diseases Loadings Variance explained in %

Air-borne diseases I 65.73 Asthma +0.97658 Bronchitis +0.86794 Eye-irritation +0.76054 Nausea +0.40626 Skin diseases -0.96915 II 24.79 Headache +0.99609 Bronchitis +0.35298 Eye-irritation +0.28610 Other diseases +0.13965 III 9.48 Nausea +0.91221 Eye-irritation +0.58287 Skin diseases -0.19472 Other diseases -0.13409

Total variance explained 100.00

Water-borne diseases I 62.99 Jaundice +0.95581 Dysentry +0.91184 Diarrhoea +0.71075 Throat infection +0.59143 Other diseases +0.42750 Cholera -0.84256 II 29.42 Kidneystones +0.99260 Throat infection +0.79779 Diarrhoea +0.68808 Typhoid +0.62924 Dysentry +0.36808 III 7.59 Cholera +0.87668 Dysentry +0.18184 Typhoid -0.77671 Other diseases -0.52907

Total variance explained 100.00 302

(0.40626) with variance of 65.73 per cent. Factor II of air borne diseases is strongly related to headache, bronchitis, eye-irritation and other diseases explaining variance of 24.79 per cent. The third factor explains 9.48 per cent of the total variance explained highlighting the role of nausea 0.91221 and eye- irritation 0.58287 in degrading health of the people.

Similarly, water pollution of Hapur results in several related diseases as given in Table-LXXXII. It is clearly observed that Factor I accounts for 62.99 per cent of the total variance explained and is positively related to jaundice (0.95581), dysentry

(0.91184), diarrhoea (0.71075), throat infection

(0.59143) and other diseases (0.42750) in degrading quality of health. Factor II reveals the impact of water pollution as diseases like kidneystones, throat infection, diarrhoea, typhoid and dysentry are positively related to this factor with a variance share of 29.42 per cent. The third factor explains 7.59 per cent of the total variance explained is positively related to cholera (0.87668) and dysentry (0.18184) as the main pollution related diseases of Hapur. Summary 303

The above discussion makes it clear that foul smell is the main problem of Hapur due to the presence of bone crushing units. Flooding of drians is also degrading habitat quality of this area. Vehicles are polluting the air of surrounding region followed by waste disposal which create nuisance for the people residing here. As a consequence of air pollution eye- irritation bronchitis, nausea and other diseases are positively associated in Hapur. Water logging is creating various problems and diseases as diarrhoea and dysentry are common here, Besides these factors, congestion/lack of open space are also responsible for degrading quality of life in Hapur.

9.9 DADRI

Dadri, a tehsil headquarter of district Ghaziabad and the city has a status of municipal board. It is situated at a distance of 17 kms. from Ghaziabad on the

G.T. road and at 28°32' North latitudes and 77<'46' East longitudes. Dadri also serves as a railway station lying on Delhi-Kanpur rail route It had a population of

32946 in 1991 of which 17742 were males and 15204 females. Location of Dadri on National highway at only 304

30 kilometers from Delhi offers good opportunities for industrial development.

Habitat quality

Factor I of habitat quality accounts for 71.21 per cent of the total variance explained. It is strongly related to garbage accumulates in heaps and drains- flooding in damaging habitat quality of Dadri with positive loadings of 0.93038 and 0.38100 respectively.

The second step analysis reveals the impact of fumes/ smoke, over crowding and drains flooding as the main item of degrading habitat quality as revealed by their positive share of 0.89148, 0.81108 and 0.56463 respectively. Factor II of habitat quality explains

25.41 per cent of the total variance explained. The third factor highlights the role of drians-flooding

(0.73214), foul-smell (0.65539) and over crowding

(0.33268) in degrading habitat conditions of Dadri with variance share of 3.38 per cent (Table-LXXXIII).

Land degradation

It is clear from Table-LXXXIII that Factor I of land degradation explains 59.95 per cent of the total variance explained and is strongly highlight garbage ao5 ro 00 0 en ^ CTl 00 rH •r > 0 X ^ oi rH n ^O rH CN OC CO 0 cn ro tN cc c CN in (N in 0 rN CO r- •cr J-) c~o 0 •H r-o in (^ ii! sT N CN TT 0 <-i r^ t^ t-- vD ro ro cc vTl in •c (0 O 0000 + + + I

c u H o tn to 10 e r^ 0 tn tan 4-1 -rt (X3 0 CU >. xz -H rH c >, o CD u Jj a tu .u c U 11 •H a a-ri 3 C rH 3 0 u O £ O t) •H tn -H cr. -H U UH V-l tu ^ C X3 CO IH 0 J-) m XI O cn 0) CO IW lU 0 01 a ID _) 4J M tU c to IW CO TD u u -r-. x: CO U rH •H 01 tD tu 01 tu -H tu D u 3 CO CU •a c ^ Q, tn -^ M ,-K r-H -H 0 •H E rH CO HH ^-> IW 0 rH -o c 3 C 0 U-J tu 0 C 0 •d ,-1 r-i 3 -rl TJ 0 !J 0 x: 0 UH 0) 0 <^- H tu Id e U ^ u 01 u fl to D OJ Ij 3 a tu XI rH X! •Si U 1) c 0 U 0 > (0 "a 00 >^ U rH In CO ^ 0 .n •H a OL, 0 0 C -H 4J to O to ^ J U) CJ CO 0) t-H Q cn o u o 14-1 •H iH 00 00 m aa r- X r~- •V "S" in Cn ^ 0 U) 0 tN in 0 1x1 4-1 C 1-t ^ •'J' rsj •V d •* r-i in cr* (^ J1 r-{ U3 t> a\ CO 00 C7> CTl ID "3" tN T) Ln n rH >i (D O 0 0 0 0 0 4J o o •J •t- -1- -1- -V •iH + + "^ rH tu o & CO CU Q4 tn cn H •d tu N H a H ti -H rH H m H 0 C tu -u a 0 a a-ri a. 01 c V-l •H 0 o rH 3 !«! a O 0 MH o •H cn X o !U a iw cj •H U TJ T3 tu 01 o to w tu tn X3 IM tu I •U tu CO H «s 01 tu j-J 3 VH M J-i c cn U U CtH to U .C to iJ -d Dl-H 3 tu tu 01 CO u 2 CQ n) cn tU C TD 14-1 r-t 4-) rH r-t M r-i 14H n 10 UH »»: (b rH O) rH 0 XJ >H c rH tu c tu o 0) 3 rH CO c e o x: ID O tH 0 •H -H >, -H tu U •H u •H tu CU VH CO to o j-j tj 01 O cn J-l CTl 01 t-> iJ tn u tn o to x> tn cn CO CO tl) tn 0 n a tu u a > tu tu XI J»i XI u 0 CO lU to U c •t~i c c O to £ t. O Q a 0 3 0 m M a 4J ^ D (J iJ ty)

K

•rl tn 00 0 t^l CTN CN 1^ vc 0 0 CO u> rH cn n 0 •* m rH 00 CO rH r^ CO ^ CO CO «J c 0 r^ U> tN 00 U5 tN CM •O" rH 0 ^ •H f»i CO [^ IN cr\ a\ VD cn CO in cn tN in r~- 0 •a •n 0 tu 1^ tu 0 •H rH tn rH d U U tu to TD tJ o tH ID 0 r-( tu x: aj t;; tu S tu XI H tu lU G (4 tu x: OJ to u 0 11) rH •rl U tu tn cn o u (0 Q 01^ tn J-l r-^ C:) iJ cn cj «< 01 cn cn tn cn u cn -H CO rH c •H H 10 C to CO c to tu 0 tn ^ (0 0 CO CO tu tu C o -ui a CO M H XI -H XI ^ Q X) 0 XI CU a U XI t) -rl V-i Ol U tu O >H E •M (0 (11 u (0 u zs z IH e U i cn a) •r^ u U 01 C CO cn C 0 lU u > iC (0 iH to 0 fC to to •H x: u CO CO •rl o ci,x5 u .c c 10 ti (D a (J u. 0 to 0 CO Q u CO 0 s > S u tn ^ cn CO D > 306 collected twice a month (0.99719), garbage collected once a week (0.99184) . and disposal of garbage on the street (0.86832) in degrading land quality of Dadri.

The second step analysis reveals the impact of domestic refuse, industrial refuse, garbage collected once a week recorded positive share of 0.96237, 0.93910 and

0.13937 respectively. The second factor of land degradation explains 27.43 per cent of the total variance. Factor III accounts for 12.62 per cent of the total variance explained is positively related to industrial refuse and disposal of garbage on the streets with their positive loadings of 0.99024 and

0.22287 respectively.

Quality of life

The result of factor analysis concerning quality of life shows that factor I accounts for 43.56 per cent of the total variance explained and highlights the role of migration (0.99236), congestion/ lack of open space

(0.52480) and absence of suitable schools in degrading quality of life of Dadri. Table-LXXXIII shows that

Factor II is strongly related to low income group people, unemployment, congestion/ lack of open space in deteriorating quality of life with their positive 307 loadings of 0.99208, 0.91427 and 0.66354 respectively.

The third step analysis reveals the impact of absence of suitable schools and lack of health facilities in degrading quality of life with a variance share of

23.59 per cent.

Air pollution

Factor I of air pollution explains 44.31 per cent of the total variance explained and is strongly related to vehicular traffic (0.93849) and coal burning

(0.50614) in damaging quality of air of Dadri (Table-

LXXXIV). The second step analysis highlights waste disposal, coal burning and vehicles as the main sources of spreading air pollution in Dadri with a variance share of 32.54 per cent. Factor III accounts 23.15 per cent of the total variance and is strongly related to bhatta units, dead body burning and vehicles as the main contributing sources of air pollution in Dadri.

Water pollution

Factor I explains 51.35 per cent of the total variance concerning water pollution and is positively related to septic tanks/ soak pits and industries as the main sources of spreading water pollution as m u> ^ 1 t~ t^ in vD 308 C O VD (^ tN X ~~ -H a> CD Ln fN • Jl X > O T3 CTi en oo 00 I rH J~ "3- •?• ^^ X (0 O o o o o 1 on O O O 1 o c + + + 1 1 (N -*- -r + — + - . + —

OS o < 01 U C -H •H 4-1 C M-J Dl to CO 3 ^^ cn C rH to u XI -u C iH -H fO iH •H -H 0) Ol e d) to H C >, M C JJ Dl-H J«i 01 U D "O "3 VJ 10 0 c (0 -ri O •-! 3 S rt (0 CJ V- X) fl J3 3 XI a 4J iJ U 0) iH >, to to m u T) ---I "O iJ D IJ T3 3 Q (0 (0 x; o to W -H 3 -D x; oj S S 3 Q J M •H 1 a + — o w •a" tn o 00 VD U3 rH in r~ •H 1 rs m U3 fN) •C rH a> r^ CO C CO (N CO U3 in po ^ m u3 0 n in <-H n 1 ^ a\ va r-: in oo ^4 (r\ in tn 00 1 in cc CO in (T\ ^ CO O o o o o 1 (M o o o o o 03 o 1 m (X + + + 1 + -r + + + h h — (U CO •H o > ti H 73 X fl to 4-1 (0 O c H to I a U U u u .H 3 o in •H r-H rH O to to r/5 tjl t-1 Ol Q,rH to § - 0) O C iJ C ro ^^ u Qj-H -H r-l I—( rH E m D X) CO C M C (0 -H 4J O (0 -H l-( (0 M ^(0 •H T3 3 '-f 3 •H C to iH to S U OJ u XI 3 XI 4-1 • H D, H) U (0 to >, tu yn to iJ rH 'H TJ HH "O (U > 3 )H JJ CO (0 x: o T3 -H to to 3 lO 0 OJ O tj 0 n) 3 O > 3 c (0 (0 H Hq M Q 3 - - d o to cr\ ^ << O ro in vD n in -H ^ rH Ol 00 in (N rH r^ en c CO u) r- o^ 1 U3 r- ro ID 00 n O U3 rH 1 f-i CN r*i f^ tN CO r-l •a m in cr> vo i m CTl CO 00 en TC 1-4 o o o o o 1 Ml 1 o o o o o t~- o + + 1 1 1 + + 1 o, •4 + + —- H u •H <>v> en < C 1 4J to C •H 4J •H p a c (0 U 1 T(UD 1I J^ u o •H Dl 1 C 1 (0 3 1 C IM C 1 •H 1 SE O <-< 1 ' s U IW H .-1 1 10 1 O to rH 1 O ' ss ifl C 10 1 rH 1 H \ O 01 1 H 1 O ^1 01 1-1 W 1 a 1 to a c 1 1 H iJ C 3 O 1 X 1 u M -rH 1 ;B a w •H ^ a 1 -l 01 H 1 rH 1 K) ttJ 1 o iJ -H O 1 1 O •H SJ 1 >J -H 3 C "O ' u • A U <-< 1 1 0* u u XI 1 O 3 X! 1 H O :^ 2 1 > 1 » to M 3 1 1 a f- 1-H > 309 revealed by their positive share of 0.92653 and 0.83725 respectively. In the second analysis industries

(0.89546), dairy animals (0.86316) and waste water

(0.52691) are the contributing items of increasing water pollution in Dadri with variance share of 33.01 per cent. Factor III accounts for 15.64 per cent of the total variance explained is positively related to waste water and water logging in damaging water quality of

Dadri with positive loadings of 0.98791 and 0.47936 respectively.

Noise pollution

The results of factor analysis concerning noise pollution in Dadri reveals that Factor I accounts for

67.66 per cent of the total variance explained i.s positively registered traffic and loudspeakers as the main sources in generating noise in Dadri with their positive loadings of 0.92673 and 0.48895 respectively.

The second step analysis reveals traffic and loudspeakers as the sources of noise in Dadri with positive loadings of 0.95335 and 0.48687 respectively.

Loudspeakers again registered as source of noise pollution in Dadri by the third step analysis with a variance of 4.32 per cent. sio Pollution related diseases

Pollution through various sources results in several related diseases that are degrading health of the people of Dadri. Air pollution in Dadri results in various related diseases as revealed from the Table-

LXXXV. Factor I of air borne diseases highlights the impact of air pollution on the people leading to nausea, eye-irritation, bronchitis and asthma with positive loadings of 0.99216, 0.94742, 0.73848 and

0.53266 respectively. This factor explains 64.38 per cent of the total variance explained. The second step analysis highlighting the positive role of asthma, headache, bronchitis and other diseases in degrading the health of the people with variance share of 22.52 per cent. Factor III also recorded the positive role of various diseases in degrading quality of health of people with variance share of 13.10 per cent.

Water pollution through various sources leads to several water related diseases in Dadri (Table-LXXXV).

Factor I explains 51.91 per cent of the total variance explained and is strongly related cholera and dysentry as the main water borne diseases recording positive TABLE-LXXXV 311 Pollution related diseases in Dadri

Factor Diseases Loadings Variance explained in %

Air-borne diseases I 64.38 Nausea +0.99216 Eye-irritation +0.94742 Bronchitis +0.73848 Skin diseases +0.53266 Other diseases -0.14532 II 22.52 Asthma +0.95462 Headache +0.95074 Bronchitis +0.59851 Other diseases +0.54584 III 13.10 Skin diseases +0.84539 Other diseases +0.82579 Bronchitis +0.31052 Headache +0.23964

Total variance explained 100.00

Water-borne diseases I 51.91 Cholera +0.99576 Dysentry +0.93986 Other diseases -0.78241 Jaundice -0.53342 Typhoid -0.52375 II 39.39 Typhoid +0.84670 Dysentry +0.34087 Throat infection -0.96340 Jaundice -0.81608 Diarrhoea -0.36016 III 8.70 Kidneystones +0.99983 Throat infection -0.96340 Diarrhoea -0.91080 Jaundice -0.81608

Total variance explained 100.00 312 loadings of 0.99576 and 0.93986 respectively. Factor II is positively related to typhoid (0.84670) and dysentry

(0.34087) with a variance of 39.39 per cent. The third analysis explains 8.70 per cent of variance and is positively related kidneystone (0.99983) as the main water-borne diseases in Dadri.

Stunmary

It is clearly observed that habitat quality of

Dadri is not clean due to over crowding, fumes and smoke and flooding of drains. Air is polluted from vehicles, coal burning and waste disposal. Water logging creates problem for the residents. Vehicles, loudspeakers and industries are the major sources of noise pollution leading to irritability and headache.

Industrial as well as domestic refuse degrades the land quality in Dadri. Congestion/lack of open space and absence of suitable schools are damage the quality of life. The water and air pollution of Dadri results in several diseases related to pollution like dysentry, typhoid and eye irritation.

9.10 M0DINA6AR

Modinagar is a municipal board which is situated on Delhi Meerut highway at a distance of 20 kms. from 313

Ghaziabad. It lies at 28'>50' North latitudes and ll^ZS'

East longitudes. The municipal limits of Modinagar extends over 55.79 sq.kms. carrying a population of

124197 consisting of 6,6996 males and 57201 in 1991.

Modinagar is a leading cotton textiles centre not only in the district of Ghaziabad but in the whole of western Uttar Pradesh. It is the second most important industrial centre of the district. Modinagar as a town is much younger than Ghaziabad. The nucleus of the town was laid down in 1933 when late Shri. Rai Bahadur Seth

Gujarmal Modi established a public limited company of

Modi Industries Ltd. on the site which was a small village known as Begamabad situated on Delhi-Meerut highway, Industrial development at Modinagar has been started neither because of a highly potential situation nor because of extremely favourable geographical conditions but mainly because Modis opted its present site for starting their industrial establishment. The main motivating factor for rapid and vast industrial growth at Modinagar was the availability of capital from Modis. Other factors as vast open tract, availability of power, efficient transport facilities, 314 adequate supply of water and abundant manpower exerted their influence in sustaining the industrial growth in

Modinagar.

Habitat quality

Habitat quality is considered as an important item in determining environmental pollution of Modinagar.

Factor I accounts for 53.63 per cent of the total variance explained and is strongly related to fumes/smoke, over crowding and garbage spread with positive loadings of 0.95730, 0.90088 and 0.60576 respectively. The second analysis highlights foul smell and drains-flooding in degrading habitat quality of

Modinagar recorded positive loadings of 0.95719 and

0.84797 respectively. Factor II accounts for 28.00 per cent of the total variance explained. The third factor reveals the positive share of garbage spread and drains-flooding in damaging habitat quality recording positive factor loadings of 0.79065 and 0.24428 respectively. Factor III accounts for 18.37 per cent of the total variance explained (Table LXXXVI).

Land degradation

Factor I accounts for 54.41 per cent of the total variance explained and is strongly related to 515 w in 00 ^ o 1^ o in 00 en yj cs o ro -^ ^ -H en • 00 00 r^ m r-l o Ti c^ [N n rH in "a" CO en n (N en 10 O o o o o o o o o o + + I 1 + + + + 1 x: U c 01 H o u H e rH (0 i a 10 x: a, m 03 01 u •H T) 01 O 0) u >, C -rl H u c 0) •H 1-1 01 4J O •H O u C 01 a-ri 3 c 3 > O r-l U 0) o E 01 •H 01 IM U 01 n C -D O 10 01 -(aU X(0J 01 01 0 01 01 U M-l 01 a U M D 4J 01 4J 01 U T) C (0 U (0 <»-l •a iJ u u x; n> (0 -H 01 0) dJ 01 0) 0u1 01 'H 01 10 4J &) 1—I l-l r-l ex 01 r-l rH i—t nJ 01 u o ••-< i-l M r-l E r-l •4-1 -^ (0 0) a o T) I-H 3 C 0 C 01 d o o o o i-H 01 r-l s •H u 10 u Tl O O o x: XI M-t o r-l •H •r| IT) 0) 1 t-( (IJ 0) (0 i-l 01 OJ j-i 01 11 -H 4J 14H •H oi 01 u tn 01 01 u u Dl J U V4 '«-ir*t a) i-i M 01 VJ T) t-l rH M Ol C U d > (0 -H 4-1 u ? 10 o 10 O (0 u u o w S U ^4 0) •M 01 r^ CT\ (T\ -H m 00 in 00 r- rH en en 00 n O (0 O o o o o o o o o O o o o o + + I 1 + + + + ' + + + I -H x: 4-) Id c 01 C o o •H (0 & e lU 10 a H (0 x: 1-1 01 H ij x> X 0) c a « 01 X O •uH Oe c H 3 U •^^ & a I n) U U M-l 01 0 M W Ol It-I 01 u C -a T3 01 10 o o -H 01 w o 0e1 Wl r-l c u rH (d •H e u o o 10 o o 10 m m u o u Dl u c 01 U •rl rH -H 01 tn (U 0) Dl iJ 01 MH > O VJ > 3 (0 (0 0) 0] 01 01 e I1 0 •d b a O b o O I o XJ XI

>1 m o 00 vo o o f^ VD r^ U) rH t~- '1' en 01 n CO r~ •"J" t- ro C~ o t~ ro U3 vo M" c r~ o in o U1 00 cn 00 n n o en CM 00 •H in o o p- 00 o en t-- m oo 00 VD m CM T) (M tn vc Ml o^ c~ VJ3 VO 00 »>< en (M rH (0 O o o o O O o o o O O o o o o 4- t 1 H3 +• + + + + + + + + + 1 4J 01 sg ^ 01 > 316 industrial refuse and brick bhatta as the main items of degrading land quality of Modinagar as revealed by their positive loadings of 0.98570 and 0.69976 respectively. The factor second of land degradation explaining a variance share of 36.18 per cent with strong positive loadings of garbage collected twice a month (0.95508), domestic refuse (0.81638) and industrial refuse (0.77247). Factor III of land degradation highlighting the role of improper garbage collection (0.98264), disposal of garbage on the street

(0.52099) and industrial refuse (0.46926) in damaging land quality of Modinagar.

Quality of life

Factor I of quality of life is strongly related to shortage of water supply, absence of suitable schools and shortage of electricity with positive loadings of

0.98062, 0.96967 and 0.23264 respectively. Factor I of quality of life explains more than half of the total variance explained. Factor II is strongly highlights the role of congestion, low income group people and migration in deteriorating quality of life in Modinagar with their loadings of 0.95762, 0.93303 and 0.89719 317

respectively. The second factor explains 28.31 per cent

of the total variance explained. Factor III accounts

for 19.60 per cent and is positively relating to

shortage of electricity, migration and congestion in

degrading quality of life in Modinagar with loadings of

0.97083, 0.33350 and 0.23495 respectively.

Air pollution

The results of factor analysis concerning air

pollution shows that factor I accounts for 55.60 per

cent of the total variance explained. It is strongly

related to vehicular traffic, waste disposal and bhatta

units in damaging air quality of Modinagar as revealed

by their loadings of 0.87002, 0.74726 and 0.61305

respectively. Factor II of air pollution explains 28.59

per cent of the total variance explained. Vehicles,

waste disposal and coal burning are the main items of

spreading air pollution. Factor III accounts for 15.81

per cent of the total variance explained and is

positively related to vehicles (0.99456) and coal

burning (0.38469) as given in Table LXXXVII.

Water pollution

The results of factor analysis concerning water pollution are given in Table LXXXVII. It is clearly tn \J3 CTl <3> U) CN in in CO CTl Oi in u) 00 •<»> CN o t- i^ •a" c ^r ^ O r3< CO CO -a* r~- o 318 •H en 00 U1 iH (J\ 00 p- ts iH T! CPi r'l r- in CJ^ r-t iH in •«< in (0 o 0 o o o o o o o o o + + 1 I + + ' + +

on o H O to Ol 0-1 3 oi c r-l i-H 01 O 01 c ^< c a c u •H u •H 1-1 D 01 Oli-i CO m w C 3 XI 4J 01 10 OJ tn m u (0 o •H •H r-H 0) D c o 3 rH 1-1 u ^^ « XI rH X) 0) XI U •H 4-1 a (0 U M 0) 1-1 m i*-i tn •H •H •H r-H O T3 U > u i«i Q 3 S M a -H M O 00 00 (N 03 U3 iH rH t^ CM d (M Ti o^ u^ f^ CO ro CO in CTl "9" r^ (0 O o o o o o o o o O O H + + +11 + + + + + O

01 CO •H O H c o on 10 c rH c (0 u O 01 en m 3 cn a c 01 o n C JQ j-i •H u •H CO o, •H •H i-M 01 03 w X> 0) U) c >, c to 01 Jii 0) SJ r-l to •H U T3 3 •H O m •H H £1 a (0 i-> •H 4-) H •rl (U 4J CO l-l tan IM to O M •uH 4-) rH T) AJ 3 4) T3 U-l 3 Qi (0 x; en 10 ID in TI iJ 3 10 "O > 0) <0 O (U J= C ID O u C U > S O Q OQ H S •J H M q> •u m

tn CN U3 in p- in in r-( in en n £71 o (N o r- r-i 00 (N ro o uj o C o r- m 03 CO 00 O •* «3 CN •H t~- •4 ^ M •M 3 u ^ O C C) u 03 O •H 0) kJ 03 T) 3 3 cm ID U Ol U u u o 1—1 10 XI XI u C 4J •H c •H on u 0) J-I M ^^ -H 10 H CO IM ID 1-1 •H u U 73 >-< & H 01 lO £ r) n •< (D (0 03 10 O c U 10 < > s m 3 o ^ Q 3 CO > a M tH > 319

observed that Factor I of water pollution in Modinagar

is mainly due to the water logging with positive

loadings of 0.57021. Dairy animals also pollutes water

of the surrounding region recording positive loading of

0.98885. Factor I accounts for 59.53 per cent of the

total variance explained. The second step analysis

reveals the role of industries 0.87706 and water

logging 0.50841 in deteriorating water quality of

Modinagar with a variance share of 24.66 per cent.

Factor III accounts for 15.81 per cent of the total

variance explained is positively related to waste water

and water logging in degrading quality of water of

Modinagar with their loadings of 0.99822 and 0.18805

respectively.

Noise pollution

Factor I of noise pollution explains 77.00 per

cent of the total variance explained. Industries and

traffic are the main sources of noise in Modinagar

recording positive value of 0.85609 and 0.71263

respectively. Factor ii of noise pollution accounts for

14.35 per cent of the total variance explained.

Loudspeakers (0.98621) traffic (0.46217) and industries 320 (0.31402) are the main sources of noise. In the third factor analysis traffic and industries again registered as main sources of noise pollution in Modinagar explaining a variance share of 8.00 per cent (Table

LXXXVII).

Pollution related diseases

Environmental pollution results in several related diseases in Modinagar. Air pollution through various sources leads to various diseases as given in Table

LXXXVIII. Factor I of air borne diseases explains 51.25 per cent of the total variance explained. It is positively related to eye-irritation (0.99938), bronchitics (0.90759) and other diseases as the main air pollution related diseases of Modinagar. The second step analysis recording positive loadings for asthma, headache, nausea and bronchitis as the main air pollution related diseases with variance share of 29.13 per cent. Factor III explains 19.62 per cent of the total variance explained and is strongly related to skin diseases (0.99400), other diseases (0.88136) and nausea (0.34442).

Water pollution of Modinagar results in several pollution related diseases that are degrading health of 321

TABLE-LZXXVIII

Pollution related diseases in Modinagar

Factor Diseases Loadings Variance explained in %

Air-borne diseases I 51.25 Eye-irritation • +0.99938 Bronchitis +0.90759 Other diseases +0.46892 Headache -0.21119 Skin diseases -0.10891 II 29.13 Asthma +0.95320 Headache +0.93841 Nausea +0.82004 Bronchitis +0.33686 Eye-irritation -0.02246 III 19.62 Skin diseases +0.99400 Other diseases +0.88136 Nausea +0.34442 Headache -0.27346

Total variance explained 100.00

Water-borne diseases I 36.52 Jaundice +0.98795 Typhoid +0.92848 Throat infection -0.82327 Other diseases -0.39266 II 31.99 Kidneystones +0.97896 Dysentry +0.96622 Other diseases +0.82050 Throat infection -0.24019 III 31.49 Diarrhoea +0.98589 Throat infection +0.51433 Cholera -0.95859 Other diseases -0.41544

Total variance explained 100.00 322 the people. Factor I of water-borne diseases highlights jaundice 0.98795 and typhoid 0.92848 as the main diseases that are degrading health. Factor II accounts for 31.99 per cent of the total variance explained.

Kidney stones, dysentry and other diseases are the main water pollution related diseases as revealed by their loadings of 0.907896, 0.96622 and 0.82050 respectively.

The third step analysis highlights diarrhoea 0.98589 and throat infection 0.51433 as the main diseases recording variance share of 31.49 per cent (Table

LXXXVIII).

Suimnfl.ry

By going through the above description it may be seen that general conditions of environment in

Modinagar are not clean as habitat quality is degrading as a result of fumes/ smoke and garbage problem of the area. Modinagar is situated on the national highway and therefore, vehicles are the major source of air pollution along with waste disposal and coal burning.

As a consequence of air pollution headache, eye- irritation and nausea are common diseases prevalent in the area which are related to air pollution. Vehicles 323 as well as industries create noise pollution. Domestic

refuse are the major source of land degradation while

shortage of electricity and migration damage the

quality of life. Dysentry and throat infection are major water related diseases of Modinagar.

9.11 NOIDA

Noida, the acronyn for *New Okhla Industrial

Development Authority' established by the Government of

Uttar Pradesh under the U.P. Industrial Area

Development of 1976 is an important industrial centre

of the district lying in close proximity to Delhi-Noida

township, extends over 3218 hectares on the banks of

river Yamuna. Apart from efficient transport facilities

and its close links with Delhi other alternation for

starting industry at Noida include various types of benefits provided by the state Government.

Industrial structure of Noida covers a wide array of items like ready made garments, textile printing, machinery and their parts, electronics and electrical goods, food products, rubber products, packaging items, tin containers and many others.

Habitat quality

Factor I of habitat quality recorded an unclean 324

environmental conditions in Noida owing to the problem

of fumes/smoke and garbage accumulates in heaps

recording positive loadings of 0.95872 and 0.91154

respectively. Factor I explains 53.66 per cent of the

total variance explained (Table LXXXIX). Factor II

reveals the impact of drains flooding, garbage spread

and foul smell in deteriorating habitat conditions with

positive loadings of 0.88184, 0.49540 and 0.28356

respectively and explaining a variance share of 35.25 per cent. Factor III is strongly related to garbage

spread (0.84334) and drains - flooding (0.40440) and

accounts for a variance share of 11.09 per cent.

Land degradation

It may be seen from Table LXXXIX that domestic refuse is the main item of degrading land quality explaining a variance share of 67.62 per cent.

Although, in few areas garbage is collected from municipal collection sites recording positive loading of 0.90452. Factor II accounts for 22.60 per cent of the total variance explained. The highest positive loading is shown by domestic refuse (0.94214) and industrial refuse (0.66742) which play an effective 335 0 rH tn Tf O ^ r- ^ ON r^ CN P- 01 ro •^ CO 0 CN rO C PO «;:r '^r r~ vr> a> i-~ O r- 00 •H ^ O <7\ as rH rH 00 t- M tN CO ^ j~^ •<1' 00 T) CO ^ C^ o o> n IN) OJ CM ^ (0 . . . o o o o o O o O 0 0 0 0 • n -r 1 in •-) + + 1 + + + + '

(U a) rH tn (U ^ d) 10 x; x; Q. 0 tn u (0 j-i •H >. 0 m O rH >, .C •rl c (1) c -H a ij U i-> •iH u 0 C a -rH tn -rl H c 3 3 U rH H (U n 01 e tn -H -rl H 01 m iH U (0 T) 10 c iH J-) X) 10 XI 0) XI 0 03 0) U 10 MJ iH 4J II) (H 0) j-j 0) 4J OS en -rl O T) C « t) t/1 10 •O 4-) 10 rH x: rO -H 01 3 01 0) -rl 3 0) 3 iJ OJ TD rH MH ft tn tn UH IJH Id VJ O 0) MH rH 11) «H e m •O 0 O u 0 3 C 0 0 UH 0) 0ao) -- I y: O 0 -C •H m o •a 0 CD M-i rH V) rH •H 0 a o H MH 0) tn (0 a) -H 10 0) iJ 01 D1 1) iz; 01 tn ^*-^ tn m 4J tn u 01 U 10 10 U 0 10 (0 C in 0 c w tn O tu 10 ID iJ iJ c •H Xi -H (1) a -H XI a; a H (u .y a U 1-1 (0 tn ITi iH F tn U .-t 0 0 tn u e •H u f", CO •ri Id (0 S-l 3 VJ m O • H u 10 O x; > O Q b4 Q Ti O Q a tn CJ5 U 1/1 CO ^ >^ at

h

CO "9" o UJ 00 ^r IN •a* t- in CO 00 "^ 0 in (Tl en 00 Lf) I-) r-l •* ro ID •"J* •o* U3 C - 0) U r~i •rH c lU .-H 11) a -u 0) rH ' C t) a •rl a ft 0 3 r. . 3 rH 0 0 Id B 0 tn -rl 0 U IW a 0) C T) iH ITS 0 a tn tn o tn a; 0) MH a o m a (U 3 0) 4J u j^ 3 •rt C T) to tn MH T3 -u u lO x; u 0 •H (0 a) 3 0) (U -H 0) 3 10 u H Tl flJ x: M-i IH a U rH 10 rH H O t-i (U E rH u UH 10 "^ M O ftr-H a ^ rH 3 C n u 0 OJ c OJ Id OS H j< 01 V (0 m M -1 u e TJ in rH u c •H 0 u c 10 3 > M (0 n (0 0 c la 0 10 o VH x: 10 0 ft 0 •d U O tl, O Q H O U o b 01 03 J CJ lA J Id

4J m tM •<><(*) IT) rg vo 00 rH CN H n Ul [^ 0 t~- in in Tj< m o fN CN V£> «»< ^ 00 t- vn -H 03 rH (\) n •sc n CM •>J< CO (N 0 01 CN r- i-H c in rH ^ rH O 00 00 1< CI CN 0 0 cn cn CN r- •H (r\ , rH •H •H U C 4-> au •H •H ft •H c: 3 •rl 0 3 r-i -rH •9 u •rl m •r4 0) 0) T3 U U rH •D » 0) TJ ID U u (0 ^ Q) (U cn C 0 (U <+l US c c 4J 10 H 0 u c b -H 10 c; o c 10 H^• nlO JJ 4J d 0 10 u •rt 1-1 ja o a-n -H u U M 0) 0 c IH e w 10 ^ 01 0 0 tn £ tl lO u u > 10 -H IH 10 b -H JC x: 10 u 10 •rt O rO Q 13 > os: w Cfl >A ;§ tn > u (0 > 326 role in degrading land quality. Factor III is positively related to irregular garbage collection even in a week (0.31646) and domestic refuse (0.21943) in deteriorating land quality of Noida explaining a variance share of 9.78 per cent.

Quality of life

Factor I explained 76.17 per cent of the total variance explained. It reveals the importance of various items like migration (0.90241), shortage of electricity (0.90043) and shortage of water supply

(0.49985) in degrading quality of life in Noida. The second step analysis highlights the role of shortage of water supply, lack of health facilities and congestion/ lack of open space which affect quality of life in these areas and recorded positive loadings of 0.97848,

0.53368 and 0.45356 respectively. Factor II explains

18.39 per cent of the total variance explained. Factor

III accounts for 5.44 per cent of the total variance explained and is positively related to shortage of water supply and shortage of electricity in degrading quality of life Table LXXXIX).

Air pollution

Factor I of air pollution recorded a variance 327 share of 50.73 per cent of the total variance

explained. Table XC shows that vehicular traffic

(0.90228), waste disposal (0.85711) and wood burning

(0.41234) are the main contributing items in degrading

quality of air in the Factor I. Factor II of air

pollution accounts for 30.08 per cent of the total

variance and is strongly related to vehicles (0.99514),

wood burning (0.87458) and waste disposal (0.51253).

The third step analysis is positively related to

vehicles and wood burning recording positive loadings

of 0.97318 and 0.25511. respectively explaining a variance share of 19.19 per cent.

Water pollution

The result of the Factor Analysis for determining environmental conditions shows that in Factor I recorded 63.04 per cent of the total variance explained. Water logging (0.90671) and dairy animals

(0.90093) are the main items spreading water pollution in Noida. Factor II explains 24.16 per cent of the total variance explained. The highest positive loadings is shown by rain water producing water logging

(0.94543) and industrial pollutants (0.49694). Factor 1 00 H VD •q' •* (N 00 •sr t^ en 1 r-( H 00 C7> 00 n o in rH ni p ro tn 0^ m [- c~ r-i 00 CO c 1 r- i/i "a* r-( o o •C (M r- 328 •M 1 cr\ (N o\ uj r»i ro .-1 o ^ in w 1 O O O O O O O o o n 1 + + 1 1 + + I + + •4

H H H cn OS u O d (0 u 3

c Ol O 01 Dl C Ou en 3 •H 01 c c XI Olr-I (^U (U Dl fO I J n->• D o 10 O i-l T3 M to 3 u (0 C <0 ^1 O > 0) 3 M S H >A a -H d CO TC 00 ro o m ^ (N •V [-- o 01 rH in in n rf a\ U} CO o •H n in •^ tN m in vo •<)< U3 o •i-t a\ c~ rH vo •"J" •3< o> as tN (0 o o o o O O O o o o o + + + ' + + 1 + +

(U n •H o a o •o en d u I n> H C M H (0 d 4J M 01 3 O O 9 •H H c jj U I-t -H Dl O 0) 10 C CO d 0) Dl M >-< c a V4 rH C O 3 01<-I (U (1) H XI •H aj3 01 (0 iJ >; O (0 C M O -H (0 (0 •H M M -H flj .-H i-t S ej •H T) 4(UJ 01 0) 3 •!-> UH TJ £i O tn u u T3 tn (0 3 (U O 10 0) 10 C IH O n> > S S !»i SMS H ^^

d o CO CO t-( •«j> '* T-t r<% c~- (^ 00 •H 01 (N iH n 00 C^ (T> 1-1 tN in tM t>- rg in u> O in CO rH c O in iH ^ o O t-- U> \o •H (T\ 00 I" in o> ON a\ CO ro •a O o o o o O o o O o + + + 1 + + 1 + + Oi u •H en

lU (0 o: ? O vs c o iH •rt to o -H H 10 eo •--v M <0 (0 c CO 01 ^< r-t CO l-< (J c 3 g* (0 j«: u Q, ca a •H X) e c ^3 dJ X en c •rt (0 >A ^ (U to •H M 0) (U • O 0 O (0 (U 0) "O 3 c t) 1 Ol rH C iJ dt CJ (U CJ rH iJ Q) c •H u. c •H u (U m rt) a u O H tH eo 10 •iH 4J "O n •H H 3: S « > • » s <0 (U a f^ •J > Q M 329 III accounts for 12.80 per cent of the total variance explained and is positively highlighting the role of water logging (0.30784) and industrial pollutatns

(0.30732) in deteriorating quality of water of this region (Table XC).

Noise pollution

Factor I of noise pollution explains a variance share of 63.10 per cent of the total variance explained. Traffic and loudspeakers registered as main sources in generating noise recording positive values of 0.86823 and 0.36158 respectively. The second factor of noise pollution is also registered traffic (0.99684) and loudspeakers (0.25007) as main sources of noise pollution explaining a variance of 27.36 per cent.

Factor III also recorded positive loadings of traffic

(0.42854) and loudspeakers (0.07817) as the main sources in generating noise (Table XC) .

Pollution related diseases

In Noida, environmental pollution leads to the spread of various pollution related diseases as given in Table XCI. Air pollution of this region results in various related diseases that are degrading quality of health of people residing here. Factor I of air borne TABLE-XCI 330 Pollution related diseases in Noida

Factor Diseases Loading Variance explained in %

Air-borne diseases I 63.20 Skin diseases +0.93991 Asthma +0.80295 Nausea +0.66493 Other diseases +0.54567 II 24.69 Eye-irritation +0.99686 Headache +0.59813 Other diseases -0.83800 III 12.11 Asthma -0.56178 Bronchitis +0.98711 Headache +0.71276 Nausea -0.73573 Skin diseases -0.32379

Total variance explained 100.00

Water-:born e diseases I 52.55 Cholera +0.97517 Typhoid +0.43556 Dysentry +0.31194 Kidneystones -0.99693 Jaundice -0.98480 II 31.13 Throat infection +0.94543 Dysentry +0.49694 Diarrhoea +0.31900 Cholera -0.14620 III 16.32 Typhoid +0.90016 Throat infection +0.30784 Dysentry +0.30732

Total variance explained 100.00 331 diseases is positively relating skin diseases

(0.93991), asthma (0.80295), nausea (0.66493) and other diseases (0.54567) explaining a variance of 63.20 per cent. Factor II accounts for 24.69 per cent of the total variance and is positively related to eye- irritation 0.99686 and headache 0.59813 as the main diseases that are degrading health quality of people.

The third step analysis reveals the impact of air pollution as diseases bronchitis and headache are positively associated and explaining a variance share of 12 .11 per cent.

Water pollution through various sources also results in several water related diseases in this region. Factor I of water borne diseases is positively related to cholera (0.97517), typhoid (0.43556) and desentry (0.31194) explaining a variance of 52.55 per cent. Table XCI shows that Factor II of water borne diseases recording 31.13 per cent of the total variance explained and highlighting throat infection, dysentry and diarrhoea as main water related diseases. The third factor is positively highlighting typhoid (0.90016), throat infection (0.30784) and dysentry (0.30732) in 332 degrading health of the people residing here.

Sxunmary

The above discussion makes it clear that fumes/

smoke, drains flooding and garbage spread are the main problems of this region degrading habitat quality-

Traffic and waste disposal contribute to air pollution which in turn leads to eye irritation, headache and nausea. Water logging, waste water from houses and

industries are polluting water which causes several water related diseases. Loudspeakers used at various functions and vehicular traffic are the main sources of noise. It also causes headache and irritability to the people. Domestic refuse and in few areas industrial refuse are degrading land quality of this region while in-migration, shortage of water supply and electricity are the main causes of degrading quality of life in

Noida.

9 .12 MORADNAGAR

Moradnagar, a town with municipal board is located at latitudes 28°47' North and longitudes 77°30' East at a distance of about 34 kms. from Meerut and a branch road connects it after a short distance with Delhi-

Meerut road. Moradanagar had a population of 44442 in 3^3

1991 with a growth rate of 70.62 per cent during 1981-

1991. The town has a regular market and a grain mandi and is involved in the trade of raw hides, handlooms and jaggery. Industrial significance of this small town owes mainly to the establishment of govt. Ordenance factory manufacturing different types of defence equipments.

Habitat quality

Factor I of habitat quality explains 72.41 per cent of the total variance explained. It is clearly observed from Table XCII that Factor I of habitat quality is strongly related to garbage accumulates in heaps and drains flooding recording positive loadings of 0.85573 and 0.76943 respectively. Factor II of habitat quality recording positive share of garbage accumulates in heaps (0.50725) and fumes/ smoke

(0.89377) explaining a variance share of 23.10 per cent. The third step analysis highlighting over crowding (0.58068), drians-flooding (0.36009) and foul smell (0.26983) in degrading habitat conditions of

Moradnagar explaining a variance share of 4.49 per cent. .^ : 1 m 334 1 cn 00 CN 00 CN in CTl n a\ 00 t t 1 C >X1 o 00 o 1^ CO r-i CN in 00 CN ID CN 1 -H o o cri CN kD •"J" •V CN VO CN in t^ ID P rH 1 1 -a 00 U3 U3 o 1 cn d o vi; rH r-- 1 1X1 CN cn •>3< VO p ro 1 (0 U1 n CN rH 1 •<}< r~ rH m 00 in 1 U) T:< n rH cn p n 1 O 1 J o o o o 1 ""1" o o o o o • cn o o o o 1 rM + + t 1 + + + + + +

+ — -1 rH ' ; x: (0 ij a 01 c •H 1 H (U 0 U cn 1 H 3 1) -H r-l 1 H x: B C cn o 10 4-1 3 >^ 11 o (0 E r-i -rl x: ! Qi 0) e Q. XJ u 01 1 O u o O Ou-rl cn 1 t* c u u VH 3 r^ 1 O O 1H Oc M to -rl 0) 1 << u r-l u I b CO T3 T) -a TJ VH (0 X3 0) Ol a 0) 0) 0) (U CO (U iw (0 c (0 U o ij u (U 4-1 4J Ol -H (U U u u u 4J CO x; •H m 1 CO C XJ x; 0) tu 0) 0) •H 3 iJ 3 ^ 1 0) •H o rH rH rH rH CO <0 rH CO 4J Id 1 i-H Ti o i-i c rH f-l r-l rH U <4H 10 c 1 ja 3 r-( •-i -rl 0 0 0 0 C 4J o l-l •H rH £> 10 (0 QJ (0 (0 0) J«i 4-1 C a 0) 10 D U X3 XI 0) XI XI r-l U VH M 4) E •H u O (0 ^j VJ (H w U rH -H o u tn 43 <§ Q [t, o (0 (0 4J 10 (0 O U x: 10 C 1 ' C3 o cn o o U CQ C/5 iJ :§ D 1' o 00 ro •.»• cn CN PH r- 1 O) CN r~ lO >J3 rH vo CN in in in rH c^ [^ 1 C t- n rH m 1 O (TV rH 1 rH cn r- •"J" 00 VJ3 a\ cn t-- CTl > in in n cn cn CN CN 1 ro p ro o U3 P 1 O O o O O CN o o o o o •* o o o O CN P ^^ + + ' 1 + + + 1 1 + + + 1 •H r-l

1 0) u c u M OJ 0) tH (0 rH rH •H rH 01 4J 0u) •H i) -H (U JJ rH rH 4J IJH ^^ C U C M J E O o x: rH rH •n o o 0) Ea CO U •H XI 4) cu rH (0 4J U 1O ,- H •d Ol CO -V. u 4.1 01 Ol O CO tn B r-l 4-1 (0 CO CO ^ (0 (0 CJ o CU -H a CO XI rH Ol l-l to o <2<§ O tH (0 10 (0 -rl O O C -H — a moo a J D 2 ^ JJ 01 -sH 01 ro n 00 o in rH in ^ yo m c~ cn r-. 00 iH c r- ^ vo cr\ M< CN CN t~ ro a\ r^ 00 •»< ro r~ in CN lO 1 in U3 00 CN) • ) & 0 • • • • 1 • • • • • CJ\ O 1 HJ o o o o CN o O o o o >«< o o o o o m 1 4J 1 1 + + + 1 1 Id + + + + + + CO -H (U 0) cu rH x: x: (0 x: O to H U 4J u O 4> >i '< •3 (U <\> >,x: •H rH 1 <^« 1 » U c u E 4-1 U 4J O C 1 o •H O c I •H to •rl a ' C I •H 1 3 •H 1 o rH 3 ' •H 1 u 4H (U 1 C • lU 1 a. 01 •H 1 o M •9 U 4J •H 1 H (U 4-1 U 1 •H 1 i-H 1 e 10 c 10 1 H (0 u O u (0 1 Cu rH -H x: (0 " (0 > H rH 1 •9 1 ^ x: C ' a 1 rH 10 rH a 1 tA to r-l a > •H 1 A "QS H 1 X • g >M tH rH U r-l X ' <4H (0 >4H 1 X 1 H 1 [j c O l-t •W 1 (U 1 2 o o O i-1 O 01 1 tu O IM 41 O 1 OJ 1 (0 1 cy •ri rH r-l 3 1 pQ U 10 U O O £ C 1 > • 1-1 (U O 1 (U 1 o l-l rH x: (U 1 03 4J O 1 43 1 H 4) B U 1 U I H (0 10 01 XI 0) O 1 Ol 4) >«H Ol-r4 1 U 1 •< Ol M CO O 1 C 1 Q CO 4J CO 01 01 U 1 C 1 S C 4-1 (0 1 10 1 H XI H rH VH I •rl 1 Q a 1 h:i CO s 1 •v n a 1 > ' e m o > > 335 Land degradation It may be seen from Table XCII that Factor I explains 49.36 per cent of the total variance explained and is positively relating irregular collection of garbage (0.80625) and brick bhatta (0.26574) as the main items in degrading land quality of Moradnagar. The second step analysis reveals the impact of domestic refuse, brick bhatta and irregular garbage collection even after a week recording positive loadings of

0.99617, 0.77264 and 0.54620 respectively. Factor II explains 40.98 per cent of the total variance explained. Factor III accounts for 9.66 per cent of the total variance and highlights the role of irregular garbage collected even once a week (0.73669) or in few areas garbage collected once a month (0.56418) degrading land conditions of Moradnagar.

Quality of life

Factor I explained 50.06 per cent of the total variance. It reveals the importance of shortage of electricity (0.99493), absence of suitable schools

(0.98377) and lack of health facilities (0.91789) in degrading quality of life in Moradnagar. The second step analysis highlights the role of congestion/ lack 336

of open space, low income group people and unemployment which affect quality of life in these areas and

recorded positive loadings of 0.99353, 0.99414 and

0.25479 respectively. Factor II accounts for 26.61 per

cent of the total variance explained. Factor III

explained 23.33 per cent of the total variance and

reveals the impact of shortage of water supply, lack of

health facilities and absence of suitable schools in degrading quality of life. Table XCII.

Air pollution

Factor I of air pollution recorded a variance

share of 43.53 per cent. Table XCIII shows that vehicular traffic (0.93047), waste disposal (0.96331) and coal burning (0.47944) recorded positive loadings

in degrading quality of air of Moradnagar. Factor II accounts for 35.06 per cent of the total variance explained and is positively related to waste disposal vehicular traffic and wood burning in deteriorating air quality with their loadings of 0.98785, 0.81355 and

0.36539 respectively. Factor III which explained 21.41 per cent of the total variance explained is positively loaded to waste disposal (0.99392), Vehicular traffic CO cn CM in U) ro o 1-1 a^ rH ^ c (N rj" •<3i t~- cn o ^ 03 rH i337 •H n CN (N •tl< CT\ CTi O XJ CTl r- 1 ro rH rr rn (0 (T> (N vD in r- n cr\ o o o o O o o o o + + t '

H H H

(6

01 01 c c •rH C 01 U m c U C r-H tn u cn D 3 tH • «H 03 m O XI (U 01 e in 4J en a 4-) Dl-H dJ j«; cn •H (0 Id 0) -D (d O C •H C O 3 r^ (0 u iH 4) •a i U-l tn tn m -H 4J O T! JJ 0) VJ lU 3 "D I-l CO ^ Id cn OJ -H m TD 3 (0 (U 4) (0 IB 10 C O o u M > s « Q 2 S Q H •J 0 -H in in a\ o c^ U) cn 00 in ro ro 00 n rH OJ o C t~ ro in H O^ o 00 in •H •H 00 iH VD Vi) 1 CJ1 >X^) UJ 'J' rH CN 4J TJ c\ 03 ro

0)

-H H H o H H a OS c H O <0 U fr> u X U 3 a i-H I rH Id H (0 o tn CO 01 01 ttr-H tn d 0 C c ifl u »H o a •H •H rH F- (U 4J •rl cn C C rtl •r( iJ •H CO •H 10 4J W C Ifl •n (U 3 ^3 1 U (0 3 U 4J XI rH XI a U •H D, iH (0 0) m I4H to i-l •H jj •uH T) rH & ItH XJ 3 o w x: o 10 T) •H rn (0 3 (0 (0 v o O c 10 (0 H O PI > s > s o 1 M Q 3 U

CO r» I-t ^ •* ro (N in 00 00 ro in Tl< n 'J' Tl« a\ rH M (N Cr> 00 o o n a\ ro H If vo ^ r- CN vo •H n u> CN 00 ^ ro fH

o Oi M -H u c o •r) 4i c T3 u a <0 Id (U 4J Px C (0 3 C CO •rt (U o § a (rt 01 O •H CO D) m 4J (0 o 4J m I oX . 3 U •s •H o c c M -H M Q, •H •H •H 0) C OlrH 4J H 4J 4J •H 9 CO c B c 10 01 10 " J (U U 1) JJ (0 •H (H tn (0 O CO ItH 10 •H U rH u •H 4J 4) 3 •H n T} 2 O OQ S > 9. S W 2 M > > 338

(0.39205) and kerosene burning (0.24226) in deteriorating air quality of this region.

Water pollution

The result of the Factor Analysis for determining water pollution shows that Factor I accounts for 63.50 per cent of the total variance explained. Waste water

(0.81412), septic tanks/ soak pits (0.44635) and water logging (0.34428) are the main items spreading water pollution in Moradnagar. Factor II explains 28.22 per cent of the total variance explained and is positively related to industrial pollutants and dairy animals with their loadings of 0.99042 and 0.66486 respectively.

Factor III accounts for a variance of 8.28 per cent and highlights the role of waste water (0.63940) and water logging (0.51941) in polluting water of the surrounding areas.

Noise pollution

Factor I accounts for 73.15 per cent of the total variance explained. The positive loadings is recorded for loudspeakers used at various functions (0.972 83) and traffic (0.43605) in generating noise in

Moradnagar. Factor II is positively related to vehicular traffic (0.84817) and loudspeakers (0.21586) 339 as main sources of noise pollution explaining a variance of 24.82 per cent. Similarly, Factor III is positively highlights the role of vehicular traffic

(0.30078) in increasing noise pollution in this region.

(Table XCIII).

Pollution related diseases

In Moradnagar, pollution through various sources leads to several pollution related diseases. Table XCIV shows that Factor I of air-borne diseases explains

60.43 per cent of the total variance. Nausea (0.85274), eye-irritation (0.58877) and asthma (0.34333) are the main diseases that affect the health of the people.

Factor II accounts for 22.07 per cent of the total variance explained and is strongly associated to skin diseases (0.96528), asthma (0.89937), eye-irritation

(0.80349) and nausea (0.39195). The third factor of air borne diseases accounts for 17.50 per cent of the total variance and highlighting air pollution of Moradnagar as diseases like nausea (0.34566) and asthma (0.27067) are positively associated in this factor.

Water pollution of Moradnagar results in several related diseases. Factor I explains 48.22 per cent of 540 TABLE-XCIV

Pollution related diseases in Moradnagar Factor Diseases Loading Variance explained in % Air-borne diseases I 60.43 Nausea +0.85274 Eye-irritation +0.58877 Asthma +0.34333 Headache -0.99656 II 22.07 Skin diseases +0.96528 Asthma +0.89937 Eye-irritation +0.80349 Nausea -0.39195 Bronchitis -0.30941 Other diseases +0.99970 III 17.50 Nausea +0.34566 Asthma +0.27067 Skin diseases -0.25457

Total variance explained 100.00

Water borne diseases I 48.22 Jaundice +0.95538 Kidneystones +0.94050 Dysentry +0.81081 Cholera +0.28035 Other diseases -0.95829 II 43.24 Throat infection +0.99965 Diarrhoea +0.94627 Dysentry +0.50490 Typhoid -0.96787 Other diseases -0.28295 III 8.54 Cholera +0.92352 Dysentry +0.29607 Jaundice +0.22434 Kidneystones +0.20166 Diarrhoea -0.24089

Total variance explained 100.00 341 the total variance explained and is positively highlights jaundice, kidney stones, dysentry and cholera as the main water related diseases of this region. The second step analysis reveals the impact of water pollution as diseases like throat infection

(0.99965), diarrhoea (0.94627) and dysentry (0.50490) are positively related in this factor. Factor III recording various water borne diseases in Moradnagar explaining a variance share of 8.54 per cent (Table

XCIV).

Summary

It becomes quiet clear that habitat quality of this region recorded an unclean environmental conditions owing to the presence of drians flooding and garbage found in heaps. Vehicles pollutes the air together with waste disposal, bhatta units and Kerosene burning. Waste water from houses is responsible for polluting environment. Dysentry and cholera are the main water related diseases. Vehicles and loudspeakers are contributing their role in spreading noise pollution which leads to irritability and headache.

Brick bhattas and domestic refuse degrade the land while absence of suitable schools and shortage of water 342 supply are degrading the quality of life. Nausea, eye irritation and asthma are the effects of air pollution in this areas.

9.13 Loni

Loni, a class III town of Ghaziabad district lies at 28°45' North latitudes and 77°17' East longitudes on Shahdra-Baghapat route at a distance of just 16 kms. from Delhi. Extending over 2.63 sq. kms, Loni had a population of 36607 in 1991 with 19853 males and 16754 females. Canals and wells are the main sources of irrigation. Wheat and gram are the principal crops of the surrounding area. At present, Loni exhibits only a limited amount of industrial development. Major factors hampering the growth of industries at this place are unfavourable site conditions and in efficient transport facilities but because of its nearness to Delhi it stands good chance for future industrial expansion if conditions are improved and the town is provided with an efficient network of transport and communication facilities. Danger of recurring floods has considerably lessened as a result of shifting of Yamuna farther away from the town. Development of civic amenities of 343 the town also require special attention to make Loni an attractive location for entrepreneurs. Habitat quality It is clearly observed from Table XCV that factor I of habitat quality explains 43.49 per cent of the total variance explained with positive loadings of foul smell (0,48429), flooding of drains (0.80047) and garbage spread in deteriorating habitat quality of Loni. The second step analysis reveals the impacts of over-crowding and drains flooding in deteriorating environmental conditions as revealed by positive loadings of 0.98762 and 0.55176 respectively. This factor explains 37.74 per cent of the total variance. Factor III is strongly related fumes/smoke (0.98883) and garbage spread (0.82206) in degrading habitat conditions of Loni with variance share of 18.77 per cent.

Land degradation

Factor I accounts for half of the total variance explained and is strongly related to brick bhatta, industrial refuse and domestic refuse in degrading land quality of Loni with their positive loadings of

0.99992, 0.99950 and 0.69621 respectively, factor II M n vD i/i o cr> m O t~ o CO Hi w CO o ^f o O 00 in vD t~- CN n CN o rH c 00 CN O iH o r» t~- ^ CN t^ »»• CN rn in •H 00 cN in i-< CN r- M o n in kO in T) CTl 00 VO rH er> CO iD in ^ rn t~ rv) rv) O o o o o o o o o o o o o o + + I I + + + I + •f 1 1

£ u 01 H C c u H O •H rH (0 H 6 (0 <0 >> • a (0 ^< ft (0 01 01 10 T3 -H •d >. 01 (U 01 c I-I •H O 4) U u ^^ I-I 01 ft 4-1 H U -H •H C 0) a a ft •H U c a 3 > o o 3 rH < O *J 0) E 01 0) 01 •H 01 ft MH U •d X) (0 C x) o k (0 to (U (U XI O 01 01 a 01 l»H ft 01 AJ U V^ 01 4J 3 M 4-) (D C u o (0 T3 u u o U (0 x: -(nd i) •H (U 01 01 01 •H 01 M ^ •H XI XI 4J ftXl r-t XI U Ol ^H M % a s> C 01 h •H (0 B k ^^ (tJ u u I-i u » Ol C o U > 3 (0 »-l 10 <0 O -H (0 0 (0 •H o x: (0 b m Q •oJ 0) O CD o o e Q o u o 2 U M J 44 •H tn CN vc 00 r-t o •«• in 00 PO o • C-- m rH rH rH •«»' TJ" O CN m O -H 00 in rn c~ in (»i t-- CN ro a\ in n CN ON a\ in 'I' iH in 00 t~- n (0 O o o •U O o o o o o o o O o o o 1 1 + 1 1 •^ 1 1 •H + + + + + + H Id j<; 0) 01 01 & 3 >i 0) rH (0 JC O 01 <0 T) 4J O 01 a >ix: 01 •H 01 CTE 4-) U rH 4-1 u 01 O •H OJ a •rH c > u u O rH a o o 01 MH •H 01 01 •H I o ^ rH a u -rt TJ T3 X3 4-1 XI 10 4J to 01 01 01 U 10 aMH Ol ft 0) 4J 4J U 01 U 3 (d C 10 I-I •H o .G •d m u u u 9 01-H 0) 3 01 01 01 01 3 IH 4-1 Id 0) CT3 £i I4H rH rH rH (0 01 OlrH 4J u 0) •H O 01 rH rH rH u 1*H (0 c tn •a o C rH u o o o 4J O <*H 01 01 01 » .-H •H r-t u u u (0 o e x: (0 o <*-< u x: 01 o 1, •H I 0) E -H 01 01 01 X) Ol 01 U HH o u 01 Ol CO 4J 01 01 014J (0 u c o rH 10 01 10 m (0 01 ;»; u C -H a > M -H jQ rH 2 XI XI XI 01 tj 01 .i< (U <0 VH 3 IH •H u 0) » 0e1 (d > M (0 O Oe u10 (u0 u(0 4J )H •oG

•H 01 en c^ rH ^ (N O rH CN vo in CN 1< t~- in 01 CN ^ 00 n (n in CN 00 m in in CO H 00 Id c •»< o rH CJ> o\ a\ vo m o 00 in n 00 00 -H CD o VO o^ ro CN rn O 'T rH in T3 a\ 00 'J' o en OO CTl (Tl VX) vo (Q O o o O o o o o o o o o o O o + + + 1 + + + + •^ + 1 1 1 Id '

•rl 01 I-* c •3 rH ft 01 c a a ft C 0 3 o •H •H 01 01 T3 a T) I-I ft U ft <«H ^ O X c ^^ X m D rH X 01 01 O 0 ft C Pu c 01 (0 C3lt-t rH 01 •H 0) O C E a o d) •4H (U 0) o O 01 H 01 a H R 1 i> (U u u •H U Ol IO 4-1 u (d < 01 01 Ol Ol c c r: 4J C (0 I-I 01 c •H H C (0 10 <0 <0 M (0 •rl 4J ft 01 01 10 H rH •H XI X3 -H •rl M E Ol O •H ffl v^ 3 10 M M >H VH Dl 3 O 01 <0 u |C c > O k (0 (0 (0 (0 iD •rl o x: c 0 a 10 SC li- Q O O > 0»Z •J CO D U 01 > > 345 which explained a variance share of 32.54 per cent of the total, variance explained. The highest positive loading is shown by domestic refuse 0.95740 and improper garbage collection even in a week 0.85834 which play an effective role in degrading land quality.

Factor III accounts for 17.32 per cent variance and highlights the role of irregular garbage collection even in few areas for a month (0.96002) or twice a month (0.86786) in deteriorating land condition of loni

(table XCV)

Quality of life

Factor I explained 71.63 per cent of the total variance. It reveals the importance of two items like migration (0.93855) and low income group people

(0.80552) in degrading quality of life in loni. It may be seen from Table XCV that factor II highlights the role of shortage of electricity, absence of suitable schools and low income group people which affect quality of life and recorded positive share of 0.99410,

0.85494 and 0.43046 respectively factor III explained

4.16 per cent of the total variance and reveals the impact of low income group people and migration as the 346 main items in degrading quality of life in Loni.

Air pollution

Factor I of air pollution recorded a variance share of 48.29 per cent. Table XCVI shows that vehicular traffic (0.98755), waste disposal (0.99153), wood burning (0.99019) and bhatta units (0.83132) in degrading air quality of Loni, Factor II accounts for

30.96 per cent of the total variance explained and is strongly related to kerosene burning, bhatta units and vehicular traffic with their positive share of 0.98818,

0.89753 and 0.38032 respectively. Factor III which explains 20.75 per cent of the total variance explained is positively loaded to vehicular traffic (0.92405) coal burning (0.71971) and dead body burning (0.43607) in deteriorating air quality of this region.

Water pollution

The result of the Factor Analysis for determining environmental conditions shows that in Factor I recorded 61.81 per cent of the total variance explained, septic tanks/ soak pits (0.84503), dairy animals (0.82749), waste water from houses (0.63167) are the main items spreading water pollution in Loni.

Factor II explains 27.ii per cent of the total variance CO in H t^ cr\ CN 00 00 o 00 cn 347 en o c^ o o rH CTl o •O" rH c •sf a^ u) U5 m rH o CT•*l (7^ -H (N H n m [-- n rH CN o U^3 "D en c^ ^ Tj< I* rH rH rH CN (0 > ^ O o o o o o o O O o O + + + I + + 1 ' + 1

o CO uc (0 u m 4J •H 3 'W •cH IW c (0 u CO 01 O ^1 01 3 01 rH c a M 4J C u m -H U •H n •H e OlrH ,n 3 C O -H to a XI r-l 3 (0 rH >H 4) () •rul o (0 3 XI XI « a -r^ u 4J >i SH CO U CO •H •-t T) 4J u On Q CQ S Q 3: M E-< ioj od -H CQ 00 m CN 00 vo •>3< t^ rH CD C^ •U Dl rH in n •* ro in CO 00 U) 00 C 00 t- o (Tl rH 00 0 -H 00 a^ 00 o 00 in n in Pr, CO T) (TV 00 n rH CT\ m rH o •a" CN o (0 o O o o o O o o o o o o CN 1 Ot + + + t + + 1 + + CN 0) n •oH a •d a uCO nJ O c I (0 M a U u o cn u 3 •H c •H •iH m C Oi CO O :3 CO >M l-l (0 (0 c rH a CO 3 U U 01 -H to n 1-1 XI -H 01 E iH (U O x> w c Ol-rl (0 - J<; Oi ^ 4CJO 0) iw CaO u > CO 3 MH T3 3 XI _ CO U •H TI to 3 o <0 <0 C (0 VH •H rH 3 P M S o 0) x: lO E-i •a >(U uO

in PO CT> (M n v o in CO in ar\ 00 o o o o O o O o o o o + + + + + + + 1 + + w •H CO u CO C H c a to T3 4J (U g (0 3 C •H MH S o 0a d n) O CO O •H o u 0) 01 CO a 4J CO •H 4J u 3 M 0) o c •uH m t) r-i H (U 0) fl u CO B C U (0 H J«! rH H la •H M 3 0) to -rl 0 10 H r-t -O 3 u 3 U 0, (U u •9 O 3 £1 (0 c a-H •H o< u u R5 « CO UH U •rt <0 Oi3 > S CO Q S M 3 3 3: OQ 348 explained. The high positive loadings is shown by water logging (0.98836) and dairy animals (0.55554). The

Factor III accounts for a variance of 11.08 per cent and highlights the role of waste water and dairy animals in polluting water of the surrounding areas recording positive loadings of 0.77312 and 0.43198 respectively (Table XCVI).

Noise pollution

Factor I accounts for 66.70 per cent of the total variance explained (Table XCVI). It is strongly related to loudspeakers and traffic as the main sources of noise with values of 0.95685 and 0.88696 respectively.

The second step analysis also registered vehicular traffic and loudspeakers as the main sources in generating noise in Loni with positive loadings of

0.43168 and 0.28887 respectively. Factor III account for 11.23 per cent of the total variance and highlights the noise generating role of vehicular traffic with value of 0.10948.

Pollution related diseases

In Loni, environmental degradation leads to the spread of various pollution related diseases. Air TABLE-XCVII 34a

Pollution related diseases in Loni

Factor Diseases Loading Variance explained in %

Air-borne diseases I 38.60 Skin diseases +0.96116 Asthma +0.67268 Bronchitis +0.21606 Other diseases +0.13408 II 37.08 Nausea +0.99361 Eye-irritation +0.99263 Asthma +0.61114 Skin diseases -0.18434 III 24.31 Headache +0.99161 Bronchitis +0.95882 Asthma -0.41773 Skin diseases -0.26889

Total variance explained 100.00

Water-borne diseases I 55.29 Jaundice +0.97346 Dysentry +0.92666 Diarrhoea +0.63155 Cholera -0.93474 Kidneystones -0.80883 II 28.75 Typhoid +0.99408 Dysentry +0.32986 Throat infection -0.92390 Kidneystones -0.57563 Cholera -0.32270 III 15.96 Diarrhoea +0.77215 Throat infection +0.31687 Dysentry -0.18027 Kidneystones -0.14872

Total variance explained 100.00 350 pollution in this area leads to several related diseases as given in Table XCVII. Factor I accounts for

38.61 per cent of the total variance skin diseases

(0.96116) asthma (0.67268), bronchitis (0.21606) and other diseases (0.13408) are the main diseases that are degrading health of the people. Factor II accounts for

37.08 per cent of the total variance and is positively associated to nausea (0.99361) and eye-irritation

(0.99263). Factor III explained 24.31 per cent of the total variance. It highlights headache and bronchitis as the main diseases with strong positive loadings of

0.99161 and 0.95882 respectively.

Water pollution of Loni results in various related diseases. Factor I of water borne diseases explained

55.29 per cent of the total variance. This factor is strongly related to jaundice (0.97346), dysentry

(0.92666) and diarrhoea (0,63155). Factor II highlights typhoid and dysentry as the main water related diseases recording positive loadings of 0.99408 and 0.32986 respectively. Factor III accounts for 15.96 per cent of the total variance explained and is strongly related to typhoid (0.77215) and dysentry (0.31687) as the main water related diseases that are damaging the health of 351 the people residing here (Table XCVII)

Summary

The factor analysis of various degrees and for various aspects of Loni clearly shows that environmental conditions of this area are not clean due to the presence of garbage spreading everywhere and owing to drains flooding. The main sources of air pollution in Loni are vehicles. Headache and asthma are the main diseases in this area which are the out come of air pollution. The major sources of water pollution are waste water from houses and dairy animals. The over all quality of water recorded as unsatisfactory and give rise to dysentry and diarrhoea in the region,

Vehicular traffic is a source of noise pollution, while in migration and low income group people are responsible for degrading quality of life in Loni town area.

9 .14 GARHMUKTESHWAR

Standing on a high cliff on the banks of the Ganga river a short distance from its junction with Burhi

Ganga, Garhmukteshwar, a municipal board, lies at latitudes 28°47' North and longitudes 78°06' East about 352

41 kins. to the south-east of Ghaziabad and 32 kilometers east of Hapur. A metalled road from Meerut joins it with Delhi-Moradabad National highway which runs at a short distance away.

Garhmukteshwar had a population of 25258 in 1991 with 13594 males and 11664 females giving a growth rate of 41.20 per cent during 1981-1991. It is a place of considerable religious importance for Hindus.

Hedsitat quality

Factor I of habitat quality recorded an unclean environmental, conditions owing to the problem of drians-flooding (0.99542) and garbage spread (0.99440) explaining a variance share of 51.40 per cent. Table

XCVIII shows that second step analysis highlight the positive role of garbage spread (0.93318) in degrading habitat quality of Garhmukteshwar with a variance share of 30.51 per cent. Factor III of habitat quality accounts for 18.09 per cent of the total variance explained and is positively related to drians-flooding and garbage spread in damaging habitat quality of this region.

Land degradation

It may be seen from Table XCVIII that in Factor I (N CO o\ a\ i-D 03 O ro 00 'T lO 01 H rf 00 '3' ro 0> en en en > O rH ro rH 353 C o'^ •* cr\ in cr\ r- > rH rH •

01 QJ (U x: 01 4J •H rH -H e 01 c 0 o a-H H VJ c 3 rH H CI 01 01 -H H ^ •H m U M T3 u (0 , rH (U M •H aj a to 01'+J •• H O XI to Ol O 4J 0" •H 01 4J ^U 10 O JJ r-< ro C 10 03 (0 tJ O 0) 01 u 10 a •H •r^ X) V^ o (0 P •H J-i C x; (0 -H c > POO Q O E Q 0) M M iJ S D

Ul CD (N U3 o 00 o 00 l-l CO CM U) 01 rH (N .H o cr\ o o en t~ t~ •H c ro r-i •"T 1-4 e(^n iH O rH rH O in •H ro O ro ro iH ^ en in r^ t-i rH o •a en r- U3 rH r-l u> •* ro U> (0 •<»• o O o o O o o o o O o o hi 1 + + + 1 + t O + ' + +

>i 01 r-H •U •H >i nO H rH JZ 0) l-l M-l 9 •H (XA< -a u n o J-l r-1 O >M a) 0 « 0) CO O % (0 0) 10 O s O (U e o' x: U r-{ 0) 0) o (1) H rH (U CO X3 •H 10 u >-l Ol M o x: -d > O ft. s w ^ •J CO •O d

in (N o u> r» o CO a> t~ ID •* n fs ^ o o o o o o o o o o o + + 1 + + + 1 + + + +

•u JJ arH •u c c •rl a a c •H u 3 o •H •rl •H 'H 0] 0) 13 u u t-l U 0) a c t C -rl Dfl 0) 10 BH X; rH r-l H JJ (U t4 <-H 10 l«-l MH o lU lU o o 6 (U 0) > OiKq ^^CO CO 5 > 354 domestic refuse and irregular garbage collection even in few localities garbage is collected twice a month are the main items of degrading land quality of this region recording positive values of 0.90277 and 0.24918 respectively. Factor II is strongly related to brick bhatta, domestic refuse and disposal of garbage on the street as the main items that are degrading land quality with positive loadings of 0.63100, 0.41978 and

0.14190 respectively. Factor II explains 28.14 per cent of the total variance explained. Third step analysis reveals the impact of domestic refuse (0.18779) and disposal of garbage on the street (0.10548) in deteriorating quality of land and explaining a variance of 21.46 per cent.

Quality of life

Factor I explains 49.10 per cent of the total variance. It reveals the importance of various items like lack of health facilities (0.99790), shortage of electricity (0.87131), shortage of water supply

(0.71094) and low income group people (0.41009) in degrading quality of life in Garhmukteshwar. The second step analysis hightlights the role of shortage of water 355 supply (0.65101), absence of suitable schools (0.41198) and low income group people (0.31072) which affect quality of life in these areas and recorded positive share of 38.70 per cent. Factor III accounts for 12.20 per cent of the total variance explained and reveals the impact of shortage of water supply (0.41093) and lack of health facilities (0.13198) in deteriorating quality of life of this area.

Air pollution

Factor I of air pollution recorded a variance share of 48.40 per cent. Table XCIX shows that waste disposal (0.96135), vehicles (0.87199) and dead body burning (0.74315) recorded positive loadings in degrading air quality of Garhmukteshwar. Factor II accounts for 35.60 per cent of the total variance explained and is positively related to waste disposal

(0.87991) and vehicular traffic (0.51430) in damaging quality of air. Factor III which explains 26.00 per cent of the total variance explained is positively loaded to dead body burning, waste disposal and vehicular traffic recording factor values of 0.54300,

0.31987 and 0.21998 respectively. ^- .„^,.,_,

1 M 0 t~- 00 00 (Tl U3 kD in 0 U3 0 03 Ol cn 0 LO cn r^ 00 cn 356 1 C ro UD rH t^ 1 T-l •"Jl UJ 1 0 c 1 (0 1 0 000 0 1 U3 0000 1 •.J" 0 0 1 t^ 1 1 J + + + ' 1 fv) + + + 1 1 (N + -h 1 rA 1 H 1

1 H 1 H 1 H 01 4J ' ei •H 1 0 a

1 CJ 01 U C -H Id •H 14-1 0 M C rH M-( 05 Id S-l (0 nj 01 01 ^ 3 W H 01 C rH 01 01 XI 0 JJ c u -H la M u 4:3 a ••A ai cn 6 c 0) m 1 CO ij Di-H Id 1 0) TS -H Id c Id 0 C u Id 0) VH 1 r-l 0 -a r-l 3 3 rH (d u 0 ' X) X3 3 JQ U •H a 1 (d (U CJ 0) ^1 N-H UH 01 1 -H •a -u -H rH U i) U U iw TD 2 1 ^ (0 cn jS Id 01 ij -H a Id 3 1 1 (0 CJ 3 s a CO H H3 0 h h h H 1 0 1 to rH 0 CTl r^ r- 0 01 1,0 cn 01 •H 1 01 cn f»i 0 CT^ o^ in r- ro cn cn 1 C CA •5t< 0 rH 00 m 0 »3< 00 in d 1 -H r- r^ i-l cn 0 rH -^r rH t-- 00 rH \£> 1 0 1 0 1 n CO in t~ in U3 CO U) ro rH t^ 00 t^ ^ 1 ID •rl 0 000 0 in 0000 Ul 0 0 r>j 1 •a + + 1 1 + + + + 4- + N 1 . — - - — 1 ft 0

m ^ n iJ H •H H •H H 0 o d OS u 1 0 •H Id H •d H I4-I 0 iJ| U i-H IM 01 Iad i< Id Id 01 01^ h 01 ^ 01 CO rH C 01 01 0 4J C 4J Id -H j«; n tH §H a a -H •rl e cn c lu (U 0 (U w w C C •rl Ol Id iJ •H i-H •H Id M 3 C 0 u Id Id XI -a --I 3 Id rH 3 u lU ItJ 3 a Id u •H a 3 •H 0) U u i>^ ti •H ID 14H 01 fH U 4J -H r-H u U i) u u IW "O iH Id 01 x: Id Id •H 4J a 01 Id 3 0 > Id (u 0 x; Id Id m Id U 0 S > U OQ Q 3 W 3 EH J

U 0) . •u — • . Id > CO 1/1 01 in 01 rH C^ r)< rH in Cn n cr> rH 00 r» P- rH rH U> cn p- 1 ^ c rH rH rO in n >!»< c~ 1 •a

0 ^ 1 iM i>V> 1 Ol 1 01 1 c I C 1 H 1 •cH I1 *J 1 •H 1 •H 1 ^ ! C 1 Id 1 •a I TJ 1 0 1 u 01 m 1 U 1 m 1 Ol 1 H 1 •H C C 1 3 1 C 1 C 1 U 1 >4H -H •H 1 ss rH 1 •H 1 2 •H 1 < 1 rH MH C Id 1 0 rA 1 Id 1 0 Id 1 b, i » 10 Id M iH 1 H 01 0 01 1 r^ 1 H rH 1 0 CO M 3 01 01 1 a 1 rH a c 1 a 1 m a • H 0 4J XI U C 1 X 1 B VH 10 •HI X 1 g u X 1 m 1 a rl -H 1 OJ 1 f4 0) e rH 0) 1 0) 1 >4 (U OJ 1 lU 1 g in u >, C C 1 ^ 4J -H Id CJl 1 ^ .^ rH 1 •H Id -B 3 U 1 dj 1 0 Id C -H 0 ( (U p 0 Id i 01 ^^ 1 Id 1 D4 01 *4 1 Id 1 V^ 1 4J -H T) U rH 1 •H 1 iJ ^ 3 0) 1 •H 1 wa 1 H Id tt) D x: 0 1 Id 1 •< Id Id c Id 1 Id 1 0 U 1 Id 1 •< S > Q CQ U 1 > 1 3: 3 a M 3 1 > 1 ss 3 EH 1 > 1 357 Water pollution

The result of the Factor Analysis for detennining environmental conditions shows that in Factor I which recorded 49.12 per cent of the total variance explained. Waste water from houses (0.97479) and dairy- animals (0.85711)_ are the main items spreading water pollution in Garhmukteshwar. Factor II explains 36.78 per cent of the total variance explained. The positive loadings is shown by dairy animals (0.81897), Water logging (0.64350), septic tanks/ soak pits (0.31079) and Waste water (0.17436) in degrading quality of water. The third step analysis highlights waste water

(0.76409), water logging (0.61956) and dairy animals

(0.13596) as the main items of spreading water pollution in Garhmukteshwar explaining a variance share of 24.10 per cent.

Noise pollution

Factor I accounts for 60.56 per cent of the total variance explained (Table XCIX). It is strongly related to loudspeakers and vehicular traffic as the main sources of noise with loadings of 0.99891 and 0.81975 respectively. The second step analysis also registered vehicular traffic (0.81899) and loudspeakers (0.76599) 358 in generating noise in Garhmukteshwar. Factor II explains 22.40 per cent of the total variance. Factor

III accounts for 17.04 per cent of the total variance explained and highlights the noise generating role of loudspeakers (0.63796) and vehicular traffic (0.41980) in Garhmukteshwar.

Pollution related diseases

Environmental pollution through various sources results in several related diseases that are degrading health quality of the people. Table C shows that Air pollution leads to various related diseases in

Garhmukteshwar. Factor I explains 64.10 per cent of the total variance and is positively related to nausea

(0.61395), headache (0.41039) and skin diseases

(0.13498). Factor II is positively related to headache and asthma as the main air-borne diseases explaining a variance of 21.80 per cent. The third step analysis explains 14.10 per cent of the total variance explained and highlighting eye-irritation, headache and other diseases in degrading health of the people.

Water pollution of Garhmukteshwar results in various diseases as given in Table C Factor I of water 359 TABLE-C

Pollution related diseases in Garfamukteshwar

Factor Diseases Loading Variance explained in

Air-borne diseases I 64.10 Nausea +0.61395 Headache +0.41039 Skin diseases +0.13498 Bronchitis -0.74300 II 21.80 Headache +0.41009 Asthma +0.13494 Other diseases -0.74198 Skin diseases -0.41009 III 14.10 Eye-irritation +0.43100 Headache +0.34098 Other diseases +0.12998 Nausea -0.34974

Total variance explained 100.00

Water borne diseases I 52.17 Diarrhoea +0.88932 Typhoid +0.81975 Cholera +0.34705 Kidney stones -0.74059 Other diseases -0.51998 II 30.10 Dysentry +0.71009 Diarrhoea +0.61540 Jaundice +0.41079 Other diseases +0.21790 III 17.73 Diarrhoea +0.97919 Cholera +0.34198 Typhoid +0.10798 Other diseases +0.10419

Total variance eixplained 100.00 360 borne diseases accounts for 52.17 per cent of the total variance explained and is positively associated to diarrhoea, typhoid and cholera as the main diseases affect the health of the residents of these areas. The second step analysis highlighting dysentry (0.71009), diarrhoea (0.61540), jaundice (0.41079) and other diseases (0.21790) with a variance share of 30.10 per cent. Factor III of water borne disease positively related to diarrhoea (0.97919), cholera (0.34198), typhoid (0.10798) and other diseases (0.10419) and explaining a variance share of 17.73 per cent.

Summary

The habitat quality of Gahrmukteshwar as revealed by Factor Analysis is not clear owing to the presence of flooding-drains and garbage spread. Air is polluted by vehicles, waste disposal and coal burning. Air pollution of Garhmukteshwar results in several related diseases i.e. asthma, headache and nausea. Water logging and waste water from houses pollute the environment. This lead to various water related diseases like diarrhoea, dysentry and typhoid, which are common among the residents. Loudspeakers and vehicles are the major source of noise pollution. 361 Domestic refuse and improper garbage collection degrade

land quality. Lack of health facilities shortage of water supply and electricity affect the quality of life

in Garhmukteswar, PART IV CONCLUSION AND SUGGESTIONS 362

CHAPTER X

CONCLUSION

Meerut and Ghaziabad districts are the most developed and prosperous areas of Uttar pradesh. They offer optimun conditions for all types of manufacturing activities and are located in an agriculturally productive area which makes one of the most active development corridors around Delhi. The study region occupies fertile northwestern portion of Upper Ganga plain which is well endowed with favourable conditions for industrial development. The growing population of the area is directly or indirectly engaged besides agriculture in manufacturing activities. Industries have helped to solve the unemployment problem created by the rapid growth of population and have helped in raising the living standards of the people. This development however, is associated with some negative environmental impacts. The rapid urbanisation and increasing concentration of industries has led to unparalled deterioration of the quality of life. Air, water and soil have undergone qualitative change not only in metropolitan areas but also in the far reaches of the rural areas. Thus, pollution as a negative and 363 harmful element in environment has become a serious problem facing the area today.

10.0 Meerut and Ghaziabad districts as pointed out earlier have a monotonous level plain composed of alluvium which is geologically recognised as old alluviam, bhangar and the new alluvium, the Khadar. On

the basis of its appearence and formation, the study area is divided into four micro-physical regions i.e., the Yamuna Hindon doab, the central depression, eastern uplands and the ganga khadar. The region has a well developed drainage system. The rivers Ganga, Yamuna,

Hindon and Kali nadi make the main system of drainage.

The Ganga and the Yamuna have their sources in the snowy caps of the Himalayas, the hindon rises in the

Shiwalik hills. The other minor streams of the area are seasonal in nature.

10.1 The study area has a sub tropical monsoon type of climate characterised by southwest and northeast monsoons. Indian Meterological Department has divided the whole year into four seasons, i.e. cold weather

Season, Hot weather Season, Season of General Rains

Seasons of retreating monsoons. The study area lies in 3&4 the broad belt of alluvial soil. The alluvial soil is classified on geological basis into two catagories, old alluviam and new alluviam. The newer alluviam of sandy nature and light in colour is known as Khadar. The older alluvium of more clayey composition and darker in colour is called Bhangar.

10.2 Industrialisation while having a positive impact on income levels, employment and production economies has given rise to many problems including shortage of housing, inadequate water supply, sanitation, waste disposal, congestion, traffic problems, air , water , noise pollution and dumping of solid wastes in open areas which get leached into the soil and ground water.

A better planning and managemet of resources is, therefore, necessary to save people from ill effects of haphazard developent but for better planning are inventory of existing resources and their utilization is the first step.

Meerut and Ghaziabad have a large concentration of large, medium and small scale industries but on account of the demand for foodgrains pressure on land has increased for livelihood for its people. About 80 per cent of the total area is devoted to cultivation. Due 365 to the massive expassion and intensive utilization of irrigation facilities, Meerut and Ghaziabad have made rapid strides in agriculture. During the decade 1961-

71, the area experienced important structural changes in its agricultural economy. One of the most important reason for agricultural advancement in this region is the availability of extensive irrigation facilities.

About 90 percednt of the total area is irrigated by canals or tubewells. The intensity of irrigation in the study region is much higher than the average intensity of Uttar Pradesh. It has been observed that irrigation from tube wells has increased by 40 per cent in Meerut district during 1960-61 to 1990-91 while Ghaziabad recorded an increase of 19.55 per cent during this period. With the development in irrigation facilities gross cropped area has also witnessed rapid increase.

The economy of the region thus continues to be predominently agricultural inspite of the fast developing industrial sector. Thus, the region is agriculturally well developed with extensive cultivation and availability of extensive irrigation facilities. 366

10.3 The study reveals that density of population in

1991 was much higher being 1044 persons per sq.

Kilometer in Ghaziabad district than in Meerut where it was 822 persons per sq. Kilometer. Meerut recorded

41.26 per cent literacy rate while in Ghaziabad, it was

44.50 per cent during 1991. The urban population in

1991 was 37.50 per cent in Meerut and 46.41 per cent in

Ghaziabad district. The study region has 46 medium and

small town areas during 1991. Meerut, Ghaziabad , Hapur

and Modinagar are the most important urban centres.

10.4 Though the economy is basically agrarian in the

study region, its agricultural development itself depends upon industrial development. Industry provides many key inputs which facilitate agricultural development . Agriculture alone can not solve the problem of the masses. Land, being a fixed asset provides employment only to a limited extent.

Industrial production, therefore, needs to be stepped up for improving standards of living of the people. The study region offers favourable conditions for industrial development. Availability of extensive tracts of level land along the major highways and a network of roads passing through the area is a big 367 boost in promoting industrial development. The situation of Ghaziabad in close proximity to Delhi coupled with the partition of the country in 1947 causing spread of people migrating to Delhi to nearby areas have acted as the greatest stimulant for rapid growth of industries in the region. Meerut has seen a large centre of industries like sugar mills, distilleries, chemical works, metal products, agricultural implements, sports goods, handloom and musical instruments industry during the last three decades. Ghaziabad is the biggest industrial area in the state and the most prominent industrial centres of the district are Modinagar, Noida, Hapur, Mohannagar,

Pilkhuwa, Dadri and Loni. These areas have major industries like Modi Steel industry. Modi Spinning

Mill, Jain Tubes, Amrit Vanaspati, Mohan Meakins, Modi

Sugar, Simbhaoli Sugar, Engineering units and several chemical and electrical manufacturing units.

10.4.1 In the study region highest concentration of large and medium units is mainly confined in the blocks of Razapur, Meerut, Bisrakh, Dadri and Loni. These are developed blocks from the view point of industrial 368 establishment. The blocks of Garhmukteshwar, Dhaulana and Moradnagar in Ghaziabad district and Jani, Rohta,

Rajpura, Kharkhauda, Parrichatgarh, Machhara,

Chhaprauli, Khekra and Pilana blocks of Meerut district have not registered any large or medium scale industrial establishments.

10.4.2 It has been observed that small-scale industries play an important role in achieving balanced economic,growth. There is a major concentration of small-scale units in Razapur, Bhojpur, Hapur, Loni,

Dadri, l^oradnagar and Simbhaoli blocks of Ghaziabad district. A continuous positive growth rate in registered units, employment and production shows that in Meerut district, the number of small scale units has been increasing from 1970 to 1990 . In Meerut district,

Baraut block recorded linear growth of 2466.66 per cent in terms of registered industrial units during this period. Medium positive growth rate is recorded in

Mawana ( 980.0 per cent ), Sardhana ( 3050.00 per cent

), Machhra( 1200.00 per cent ) and Meerut ( 603.39 per cent) . Parichhatgarh and Baghpat blocks recorded low growth in terms of number of units during 1970-1990.

A continuous positive growth rate in employment 385 during 1970-1990 shows that Baraut recorded highest

rate of gwowth ( 1453.33 per cent ), while Meerut

(131.47 per cent), Binoli (70.58 per cent) recorded

medium growth. Parrichatgarh, Mawana, Baghpat and

Machhra block registered low growth in terms of

employment during 1970-1990 . As far as production is

concerned, highest growth was recorded at Baraut while

low positive growth was recorded in Kharkhauda block

during 1970-1990.

10.4.3 In the study region, polluting industries have

been identified by the Central Board of Prevention and

control of pollution. These industries are chemical,

sugar, distillery, tannery, pulp and paper, textiles,

dye stuff, fertilizer and pharmaceuticals. In

Ghaziabad, 75 units and in Meerut, 27 units are polluting the environment. The main industries

discharging their wastes into Hindon and Kali nadi

are Sugar factories, distilleries, Khandsari units,

chemical, pulp and paper metallurgical, and processing work. The river water is of course most polluted due to

the uncontrolled discharge of sewage and industrial

effluents in the study region. ?70 10.5 . The impact of industrialisation on environment is

seen by studying various aspects of pollution in the

study region through the technique of Factor Analysis

in respect of habitat quality, air pollution, water

pollution, noise pollution, land degradation and

quality of life. The first analysis deals with the city

areas of both Meerut and Ghaziabad districts while the

second analysis deals with several aspects of

environmental pollution in selected towns and urban

areas of the study region. The environmental pollution

of the region ultimately leads to several related

diseases that are degrading health of people in the

study area.

10.5.1 The results of the first factor analysis

concerning habitat quality shows that flooding of drains, foul smell and garbage spread are the main

causes of degrading habitat conditions in the

localities of Meerut and Ghaziabad city areas. Domestic

refuse are the main causative factor of land degradation. The other items that also play an effective role in degrading land quality are garbage

collection once a week and people of these localities dispose their garbage on the streets. 371 In few areas, garbage is collected through municipal collection sites but their process of collection is quiet irregular. Shortage of electricity, shortage of water supply, lack of health facilities, low income group people and congestion / lack of open space are the main contributing items in degrading quality of life in both city areas of Meerut and

Ghaziabad. Vehicular traffic, waste disposal, coal burning recorded their positive share in increasing air pollution. Water logging, waste water from houses, dairy animals and industries are the major contributing items spreading water pollution. The main source of noise in both city areas are vehicular traffic and loudspeakers.

Environmental pollution through various sources giving rise to many pollution related diseases which affect people living in these localities of Meerut and

Ghaziabad districts . Air pollution of these localities results in various related diseases that are damaging quality of health of the people. Asthma, bronchitis, nausea, eye-irritation and skin diseases are positivety correlated in the localities of the study region. Water 372 pollution leads to many diseases that affect the health of the people. Diarrhoea, Jaundice, throat infection, cholera, dysentry and other miscellaneous diseases are the main water-borne diseases of the study region.

10.5.2 The results of the second Factor Analysis for various aspects of pollution are given through Summary

Tables in respect of habitat quality, land degradation, quality of life, air pollution, water pollution and noise pollution. Environmental pollution results in various pollution related diseases that are damaging health of the people in the study area.

10.5.2.1 HABITAT QUALITY

It is clear from Summary Table CI concerning habitat quality of Meerut district that flooding of drains and foul smell causes the main unhygienic habitat conditions in all the sampling points except in Daurala where it has no impact . Of the remaining items affecting habitat conditions, over crowding plays a leading role in Abdullahpur, Mawana, Daurala, Baraut and Baghpat stations, garbage accumulating in heaps degrades habitat conditions in Abdullahpur, Mawana and

Kharkhauda stations and garbage spread every where damages habitat quality in Abdullahpur, Daurala, Baraut 373

H CO H

< < H o E it^ftnioivDiooitNitNi rHiiniaoiiriini«3X> 0) iCT\ivDit^ii-(iCNi<-ircr\i a^lCJ^lool^ola^lOl(Tll^x> e lOlOlOlOlOlOIOI OlOlOlOlOIOlOlO D l + l + l + l+lll + lll +I + I + I + I + I + IIII

M H OJ lrHICNlOIOOIVOI"i)icr>i^ivciiJi'<}< 1 £) (U SZS 1 U U H 1 (0 a lOiOlOlOlOiOlOl rOlOlOlOlOl lO 1 o m l + lll + l + l + lllll l + lll + l + l + l 1 +

H en •:] a •«i! (t(U3 1 £ D looiooiooiLniinicTvicrii ini'S'inirHivoioicrii a • •5j^i'3'i ooir-iooiooikoiLDitNiiJ itNirHioini<^icr\i(r\i ooivnicNiuiitnifNi'^iM U U 1 g (0 lOiOiOlOiOlOiOl OlOlOlOlOlOlOl H O i + i + iii ( + 1 +III + 1I1II + I + I uH) m•4: *n< H n

H H Cn icNicNir-ioi^ivDi'^i'i LTii'^riiniooiiHioii.oicri it--i'^iir)icr>ir-icoi(Ni ij3i<*itNiaoic~-i

M

f—1

H F—1 OJ OS E 'r^iLTii icniooi'Tirni oicniLnirHicTiimimi m i-iiCTii ccnicTNi«3iiaoi rHicOiiWit^iminiroi o >-i

U O 11.11 1 1 1 , 1 , , s a^'iiii^i II I Di 1 1 1 1 i u u ,J.<.JlHl<|<'SCl•'^'0c;iVi-HOiaiMi2r I

and Sardhana. Fumes/smoke recorded positive association with polluted habitat quality in all the sampling

stations except Sardhana and Kharkhauda.

Like Meerut, flooding of drains is a common phenomena in all the sampling points except Babugarh of

Ghaziabad district. Over crowding disturbs habitat

quality in Babugarh,- Hapur, Dadri, Modinagar and Loni

areas. Foul smell creates problem for the residents in

Babugarh, Hapur, Modinagar, Loni and Noida while the

remaining stations Dadri, Moradnagar and Garhmukteshwar

are not affected in this regard. Garbage found in heaps in areas of Babugarh, Dadri, Noida and

Moradnagar while garbage spread on land creats nuisance

in Hapur, Modinagar, Loni, Noida and Garhmukteshwar.

Fumes/smoke is a common phenomena and are affecting the living conditions of all the sampling stations except

Moradnagar and Garhmukteshwar where they do not degrade habitat quality.

10.5.2.2 UiND DEGRADATION

It is clearly observed from summary Table Cll that domestic refuse are the main causative factor of land degradation in all the sampling areas of Meerut ui m

KUUO l^^l^ol<^l(^^nlff^"M• r^iM'r-^it-i.mio^iOiM «l>>> I -fl .•! i + ll.tl U — — — — — -f — • — • — + — • — • — • — • — — — • — + — * — • — • — * — • — 375 H Pi Q I I I I I ( i I . . I r . I i H ti]Ci]<4 t^0|^^•OlO^tOlO^•tf^• i/tiiri9i*tf>vjD< •tAicO W

Q^,4MO tOln^Ol^^i/lt0^lUll 0^tr••0^>0^leO•0•CO•fN n:a3i: ••••i-i •••,-.•. .,.,. „,.,. OOH I0,"0<0i0i0i0t0t OtOiOtOiOi -lOiO

— — — — — 4 — + — + — + — 4. — + — « — • — — — • — • — 4 — • — • — 4 — + —

H O I I I t • < < I I t I 1 I 00 < I < OH a ioioO"irttoot(^im

w ajzs i<0> a — — — — — + — •» — + — + — + — + — + — * — — — 4 — + — 4 — + — • — + — • —

ox I i . I I I I . . i I I c . I tA H K iVDiOiniONir^irotO' iO'i/itf^iflO"Mi-Hi-H P UHQ iMijniotoif^isfltuii ivivtcO'-a-iMif^i'n (< H <.JW ...I z ' H UO> lOiOiOtOiOtOtOi 'OiOiOiOiOiOiO s UU tii + iiitii t^-.ii+i + i^-iiii

o Q II.,.,.. ...!,,. OHXH iO,(N, , ,mt(T,, , (N,fl0,ui,OtO.r^,r»,ff\ H «J,^,o,o\,,^, r>iO,ui,0\,(N,r^'^,ri ce^JEDi ,7(,vfl,MiHiu),oo,M, o\,^,r^l,0^,0^'O),^.vo rf! •

CD H H H Q CJ z , , I I I I I I I . ! ! . ! . OiJO.ii,,,,, ,,,,,,, Q uu<ir~i«r,r-,oi9t,9i, n<ui,-^,OOin,niMive, Aiff\,votO,u>,m,\o,'H <

w i,H,r^,m,(0,|, o,4/),r-)io),9t,,A,^iao &,;*< ,,n,a^ MH ,U>,H,rtlUl,VD,C0lO^, Hl*,0\,Ul,CO,V,l/l,M o!,< ,r-,n,y»,ia,(ni\©,(^, oi^i9tiA,^,ui,Hix|, w n X ,',',',.,.,.,., , . , . S QQ lOloiO, 010,010, 0.0.010,0,0,010 u • + <,, + ,-f,«,«l,l ,,+.,,,, + ,,,4-,+ H H

Pi >J . . I , , , . . 1,1,,,, >« .1111,.. . o MCd lAini looiwi^i . ^iO,oii^iO,r^,,H,0\ h QCo) tniM, io,<#i«< I \Air),ooi,r,u>,^,^.M HD iniw. i .,.,. O Z iO.oi .010.01 I oioto.oio.oio.o H •-* ...i... I ,t + ,«i + i4-i4-.i.,

O H1 U •t^iO\,fl0.eO.Ln,Ot9ii 9iir4,r^,mi0.air^,V w irii.eOiUlfrHiMti/iiO, '^•9t,r,timioo,r-i^i^ HM i*.0\iO.ff»iin.*i«i o«n,ciiiDi\Dto.,£ir*) O vx VI .ao.9t.,(r(t,H,et'U>iVt.iA I IM I • , , , . I . O Oca .Oio.oioioioio* 0,0,0,0.0,0.0.0 << QOi .•,+, + ,+,•,•.•. +.-f.«i4, + .-f.-t-i +

H ...... ,, ,,,,,, I K O , o: ,,,,,, , ,,,..,. X »»; u ,D, , , , , .i Bc ,j.2'«:.DiSio.'»i;.n-Ho.o:.M.2, ,^,Q,I •HO ,D,rtiB:.<><<>«ai,o.,o.a,Z'>-<.a:iK .(a.««,<<,,<.«<,<<.s.-«x:»<.<<.<,o.o.o.O'< .<<.£.a,a.v),m.s<.aoai.£,a,£.j.z.z.o 376

district. The other dominating item of land degradation

is garbage whose irregular collection once a week

causes degradation in Mawana, Daurala, Sardhana,

Baghpat and Baraut. Garbage which remains on the roads

or on the streets for fifteen days or in few areas for

a month also generates nuisance and thus degrades land

quality in Daurala, Sardhana, Baghpat, Kharkhauda and

Baraut of Meerut district. People of Mawana, Daurala,

Sardhana and Kharkhauda besides disposing off their

garbage on the streets also throw it away in the nearby

drain. This is a common practice which helps in land

degradation. Besides garbage, brick-Kilns also degrade

land of their immediate surronding in Abdullahpur,

Daurala, Baraut, Sardhana and Baghpat. As against these

items, industrial refuse does not play their role in deteriorating land quality of this region.

In Ghaziabad district, domestic refuse is

responsible for degrading land quality in all the

selected stations. Similarly, industrial refuse plays a positive role in degrading land quality of Hapur,

Dadri, Modinagar, Loni and Noida areas while brick- bhattas degrade the land in Hapur, Loni, Moradnagar and

Garhmukteshwar. Garbage is another item of land 377 degradation which affects land if it is not collected from municipal collection sites in Babugarh , Dadri,

Modinagar, Loni and Moradnagar or even if it is collected directly from the street in areas of

Babugarh, Dadri, Loni , Noida and Moradnagar. In some places like, Babugarh , Dadri, Moradnagar and

Garhmukteshwar of Ghaziabad district, garbage is collected everyday but its rate of accumulation is so high that it degrades land quality. When garbage remains on the street continuously for a week or so it of course damages land mainly in Babugarh, Dadri, Loni,

Moradnagar and Modinagar areas. People of Babugarh,

Hapur, Dadri, Moradnagar and Garhmukteshwar areas dispose off their garbage on the nearby streets and thus contribute their share in land degradation of their respective areas. In some other areas like

Hapur, Loni, Noida and Moradnagar, people throw away their garbage in the nearby drain and this too destroys land condition.

10.5.2.3 QUALITY OF LIFE

Summary Table Clll shows that shortage of electricity and lack of health facilities come out as CO 378 H u 0 a ' a ' 1 ' ' ' H 0"<^' i/)imi»'(N'mi*'ff*''^ as IB • r^ • r- ' 4 < -v , ~t 1 ^ > v • yc ^i(V)i >Hi<4'i(rii«0'U>ir*>i^tC^ i • > < •H 1 1 1 • 1 lootr-i fHiOtOiiniOtoiM'r-

ir-iu>t p.ir-(M>!H>*ioi.«»ir-^ H (T\ t a\ t (si

a 1 1 1 1 1 § VI 1 t . t -H 1 00 1 0\ 1 O 1 UJ < (NiC4iOiVO>tf (M 4jioair4ir4io^iu> Jiir-^-r^l^Ol00t«)"^'<^ i

ij 1 1 ( 1 t C , , . 1 t V . 1 < . 1 E . . > . • >, I 1 r* 1 (N 1 O 1 00 -timi Hi-HiOi-Hiot t^.r- 0 ' • 01 ' 1 r- VCiOli Hi

H 0) , , . . , u E .I.I. 0 1 ^ 1 tf 1 ixi 1 O . \D r^iOt Hi^.a)"ro'niOi«*.o I U r- > M 1 V 1 V . ^ (Ti.Oi ^ir-to.o*r^.9\i^.Ti' C • ~* 1 \c 1 f^ • 1 9\ 1 If) '^.r'l -^llN^^^lMlr-.oo^.^flO u a MCii 'tfii/ii-H.r^iui 3 0 ,.,.,..... n 0^ .C.OiO.OiO OiOi OiOiOiOiOtOiOiO JO 1 + 111*. + .. + * + . ll + ) + l + l + ... + l + < iz: H H U H 4^ '1.11 h 0 . . , OJ 1 —( . L/> 1 (XI . ^0 tf\ 1 CO i •HivDiOif^i'tf'inimtoo fti r-t C VC 1 (N ro 1 O ui.-^i , , , ^ O'Oi OiO.OiOiO.OiOiO H + . + ( ,, + , + 1 + , + ,,. + ,+ H

C 1 • . (^ ^^ aj < . , c a , . . , O 0 0 • . . , h •-1 C OC 1 OC • V ' OC . 1 >\Otn> iJ ^M — »r ' V ' V > i/> . i >xfi>r>>ryi tn i> 1 -^ -H 1 o [^ . ^ o ^xo c^- 1 t^ia\i\OiO\ii<7\i^tMiO'00'H ^ . •-( r" I CT" o> - ^ b* . 01 2 • • ... • . 2 ...... t ...... u c -« o ' c • o . o Oi . O.O.OtOtOiOiO'O < • 1 . .t + . + l + l + . + .l..

1 . 1 . 1 .... (i: u . . . , . . . rf o . , 1 1 .3 a . 1 ...... 1 I •4: w :; • 1 ' («(. . . . . , .QiiW Pi u a. : . ' Q" -0 . • .CC' ' .rt:.W -w ij r: . 1 • < . D'iJflX' ' •<• ' -U'H a V< D < > < > -2 > ij i^ -^ . < . J h . -< <.Xt.H««i;. 1 > < > . -Z'D o u ^ - z ' < D ' X a."«.^-HO'atH.z< > < i o > s: •H 4) z: • < ' X < > a X ' X (aJND'D'tf'tH.tH.Qi^t <.<u:Qj.Z'z:>u 379 major items contributing their share in degrading quality of life in all the sampling stations of Meerut district except in Daurala and Mawana where they play negative role in this regard. As against these items unemployment problem has no impact in affecting quality of life in all the sampling areas except Baghpat. The remaining items concerning quality of life have different influence on different stations. For example, shortage of water supply degrades quality of life in

Mawana, Daurala, Baraut, Baghpat and Kharkhauda stations while low income group people residing in

Abdullahpur, Daurala, Baraut, Baghpat and Kharkhauda deteriorate the standard of living of these areas. The absence of suitable schools is a problem of Daurala,

Sardhana, Baghpat and Kharkhauda while congestion and lack of open space affect life in Abdullahpur, Mawana and Daurala. In migration is also a source of degrading quality of life in Mawana, Daurala, Baraut and Baghpat while in remaining areas of this district, quality of life is not affected by in-migration.

Shortage of electricity is the main item in degrading quality of life in all the sampling stations in Ghaziabad district except Babugarh and Dadri. Lack 3S0 of health facilities are positively related to quality of life in Dadri, Moradnagar and Garhmukteshwar areas.

Shortage of water supply is a problem of Babugarh,

Hapur, Modinagar, Noida and Garmukteshwar areas. As against these items, unemployment is not the main contributing item in degrading quality of life in all the sampling areas of Ghaziabad district except Hapur and Dadri where it plays a positive role in this regard. Low income group is also deteriorate the living standard in all the sampling stations except Babugarh and Noida. Absence of suitable schools contributes their share and creats problem in areas of Hapur,

Dadri, Modinagar, Loni, Moradnagar and Garhmukteshwar.

Congestion is problem of all the sampling stations except Loni and Garhmukteshwar. In migration is the main cause of degradation of quality of life in almost all the sampling areas of this region except Babugarh,

Moradnagar and Garhmukteshwar areas of Ghaziabad district.

10.5.2.4 AIR POLLUTION

It may be seen from Summary Table CIV that vehicles and wastes materials are the main items which 381 to H U H 1 \^ 1 U3 U5 1 O 1 O 00 1 ro rr l'>;} 1 CN inif-ir-iiniixjiinirHim 1 IX) 1 r~ r- 1 r- 1 r- cn 1 r- criir~-i[^io^it~-icriit^iin

x; 1 O 1 O o 1 O 1 O o 1 O OlOlOlOlOiOlOiO 1 + 1 + + 1 + 1 + + ' ' + I + I + I + I + 1+1 + I + Q > + + — + — + — + — -1- — + —

H 1 n 1 CN o 1 1-1 1 t^ n 1 1X1 lOirOlrHICNl I'J'IO 1 rH 1 ff\ o 1 O 1 rH n 1 IX) iroit^iCNicJ^i i«i*'icriiroini,Ji(Niin » U 4-1 r O 1 t~ vo 1 m 1 in !t • £ C 1 O 1 O o 1 O 1 O o 1 O lOlOlOlOl lOlO a CQ D 1 1 1 + + 1 + 1 1 1 1 1 1 1 + 1 1 1 + 1 1 1 1 1

+ — + — + + — + — - • — + — < — H P PS 1 rN 1 00 CN 1 CN 1 rH rH 1 in OOlOl^lCNirOICNlCnit^ H 1 CN 1 1 P TT 1 r<\ 1 O 1 CJ^ in 001 iix)i^it-i iroirs O m 1 O 1 CN 1 rH 1 00 in CNl l>lOlOl l^lrH a £1 c 1 t~- 1 in 1 a\ 1 n 00 fNl llXllfMIU5l l •H 1 •^ 1 in h-l 1 uj 1 n r- 1 i-J rH it-Piooiooiroijir- 1^ o T) c 1 1-H 1 CN H 1 •q) 1 O r- 1 M 00 IMICrillX)l^lMICJ>IU3 H p< (D u 2 1 3 . 1 S 1 .1 .1 • 1 !s 1 • 1 • U (U a 1 o 1 O 1 O 1 O o 01 lOlOlOl lOlO Q £ 1 + 1 + 1 t 1 1 + II l + lll + l 111 + H + — + — + — + — + — - + — pq •< o H H H U 1 00 1 1X1 in 1 CTl 1 CTl 1 t-- 00l[^l'>J|

1 LD 1 * iinicNiCNicr\iooiroir-j 1 00 i iH r-l 1 r-i 1 CTl CM 1 00 ^-lOlcnl^^^lr-la^llnlrH b 1 ID 1 O 00 1 m 1 a\ 00 1 00 rolOlCNiCNirHirriOilX) 1 m 1 iH in 1 CN 1 a\ rH 1 CN rHlOliniOlCTilCTliCNlin CO c = 1 O 1 O o 1 O < o O 1 O OiOlOIOlOlOiOlO u x: 1 + 1 1 t 1 + 1 + + 1 + + I + I + II1 + IIIIII H + — + + — + — + Hh + Q O 1 ^ rH h^ 1 O '!< 1 00 1 00 1 in c7\iroiix3i[^ia\irHimiixi 1

• Ci II a: • D 1 < 1 1 1 1 1 1 a 1 c/3 1 Q4 1 Q Ti 1 1 1 Di 1 1 1 < 1 W U ' X < 1 D 4J(oa:i 1 i < uxic^i 1 lOi 1 < a: < u!. 4-1 J-. '< < i H IS •H m H-H OlOilMlSl l<:iQlS •r-l (U 2 1 S1 3d a 4JNtllDlQ!lMlHlQliSiS a 5: 1 O § 1 ^ g 1 g •Hx;

Meerut district except in Kharkhauda where they play a negative role in this regard. As against these,

Kerosene burning no where affects air quality. The other items considered for assessing air pollution have varied influence on different stations. For example, wood burning and coal burning pollute the air in

Abdullahpur, Baraut, Baghpat, Sardhana and kharkhauda while they do not damage air in Mawana and Daurala.

Brick kilns have their own polluting influence in

Mawana, Daurala and Baraut while in other stations they in no way disturb the air quality. Dead body burning is not a daily feature but where it takes place it gives rise to slight air pollution in Abdullahpur, Mawana and

Sardhana. The air of the remaining sample stations is unaffected by this practice.

Similarly in Ghaziabad district, wastes materials and vehicular traffic are main items causing air pollution in all the sampling stations while remaining items concerning air pollution have different influence at different stations. Wood burning pollute the air in

Babugarh, Loni and Moradnagar while coal burning are positively affecting quality of air of Babugarh, Hapur, 383 Dadri and Loni stations. Kerosene burning is in common practice and polluting the air in this regard except in

Dadri and Modinagar where it is negatively associated to this item. Dead body burning is not a regular phenomena but where it takes place it affected air quality of Dadri, Loni and Garhmukteshwar region. Brick kilns have their own polluting affect in Dadri and Loni areas. The air of the remaining sample stations is unaffected by this practice.

10.5.2.5 WATER POLLUTION

Summary Table CV concerning water pollution shows that waste water from houses is the main item spreading water pollution in all the sampling stations of Meerut district. Water logging is also a problem in all the areas except Sardhana where it is negatively related to water quality. Over flowing of septic tanks/soak pits are responsible for polluting water in Mawana, Baraut,

Sardhana, Baghpat and Kharkhauda stations. Industrial waste water helps in polluting water in Mawana and

Daurala stations while dairy animals do the same in all the sampling stations except in Babugarh.

On the other side in Ghaziabad district, waste to H 384 U H OS H M

1 cr^ 1 O H 1 O 1 CN 00 1 cr> 00 r- CN O CN o 1 H '* I ">a< 1 CN 1 CN U) m in m in CTl r 00 H 1 a\ 1 00 1 00 <1)-H 1 VO 1 O U) in •* r- O ro ro vr) 1 ro C3^ 1 (Tl 1 H 1 in 1 Ol 1 CTi 1 IT) 1 in (T\ 00 CN 1 CN ro r- 1 H 1 00 1 H 1 ro 1 a\ (0 Cn 1 a\ 1 rl< O U) H r- 00 ^ en H 1 O CN 1 r- 1 ^ o S O 1 O 1 O O 1 O O 1 O O 1 O o O 1 O t O 1 O 1 O 1 O 1 + 1 + + + 1 + + + + 1 1 1 + 1 + 1 + +

r + h r h h >• h r h h h— H D (kS H H m 1 KO 1 00 1 00 1 CT\ a\ •* 1 ^ '4' 1 O 1 in 1 O 1 H 1 U> 1 H S 1 Tjt 1 -.[f >>.rH r 00 n H o ro r- 00 00 1 00 o 1 0\ O 1 n 1 t^ UJ r-l in ^ lO CN a\ 1 00 in 1 CN 1 r- <* is -H e 1 CN CN i^ O a\ iJ VD H H CN 00 o H ro O H rC-H 1 (N U> c^ n in M in H a\ CN CTi VD >* O VD a c 1 O O o O o o O o o o o O o O o 1 1 + + + + + 1 1 + + + + 1 1 H H +

O > U rt jj 1 00 H en o t^ 00 H in U3 ro ro CN > S-i (C 1 a\ ro CN o in • C3^ in m U) VD H •H^ 1 •.jt •* C^ CN 00 m in in o CN t^ •<<' r~ '* H t4 ^ m 1 H

to o z 1 (J\ (y\ o H c^ H in ^ H 1 H c- i-( 00 in r~- r- ro in •^ UJ no VD CN r~ Q 1 CO r^ VC in C3^ n o in V£) r- CTi CN •* H r- •4! <\) U 1 (J\ VD H as •^ 00 o VD r- in vo O : •H iJ 1 ffi P 4J (Offi O H 1 < < <: 4J ^( H < M < a a < > ^ 9 g W 0) 1 J ft 1 i4 H < > •H (U 1 D < s. a, W 1 g , M 1 M P • OS 1 Q S 5 ' "^ ' to (OCQ 1 ft 1 P 1 S M P2 I C*^ ' CQ < > < 1 POPQ 1 S 1 P 1 S 1 a I S 1 S 1 O 385 water from houses is the major contributing item in polluting water of all the sampling stations except

Hapur and Noida while water logging creates problem and pollutes water in Babugarh, Hapur, Noida, Loni,

Moradnagar and Garhmukteshwar. The remaining stations of Dadri and Modinagar are not affected by this problem. In this district septic tanks / soak pits also pollute water quality to some extent and thus pollute water in Babugarh, Dadri, Moradnagar and Loni.

Industrial waste water damages water in Hapur, Dadri,

Modinagar, Noida, Moradnagar and Loni. The remainging areas of Babugarh and Garhmukteshwar are negatively related to this item as there are no registered industrial establishments in these areas. Dairy animals in Dadri, Moradnagar, Noida and Loni play their positive share in deteriorating water quality of these regions.

10.5.2.6 NOISE PULLUTION

It is clear from the Table CVI that vehicular traffic is the main source of spreading noise in all the sampling stations of Meerut district. Loudspeakers used at various functions stand in second place in generating noise in all the stations except at 38B

CO 0) •H u 1 CTi cr> CM o o a\ o in Ti< r- vo c- H cn 4.) 1 ID CN in a\ 00 CN r- o en ro 00 r- ^ U) 1 >J3 r~ 'it 00 CO o 1 in c^^ o rvj \D r- 00 1 in H fs cr> (N cr> 1 ""t ro •^J" 00 CN 1 H3 o •^ H CN H H 00 M c 1 cr\ r- in in m H in H H in 1 O 1 O 1 O 1 O 1 O 1 O 1 O 1 O 1 O 1 O 1 O 1 O 1 O 1 O 1 r 1 1 f f 1 1 1 1 1 1 1 1 1 1

+ r h h h K m ^^ X 1 U3 o in 00 >J3 H en in in m 1 •^ Lf) en VD LD n VD CN ro * en o ro cn U5 o in 00 I o 1 O o o o O o O o o o o O o o o 1 1 + + + + .+ + + + + + + + + + —^. L J + r "1• ••"—" - —

u 1 (y\ 00 CO o t^ o U3 CN CN ro ro •H 1 •<* H ro CN LO in <* in en o in 00 in ro ro y-i 1 vx> fNJ fM 00 00 in U) CN o o r- 'J' ^ 00 Ch r 00 iH (Ti 00 VO H U) CN > •>* u) 00 U) CN H 05 1 r~ r~ Lfl CJ\ CTi 00 U) en a\ in ro t^ in CO >^ E-i 1 O o o o O o O o . o o o O o o o 1 + + + + + + + + + + + + + + + 1 1 J L ___ J 1- • — - h— + f- r • h— a 1 1 a X 4J 1 D < Oi C/3 O 1 04 T) Pi -^ ^ J £-1 < s •H to (< < D m (V 1 J B ID ' 5sC ft « 1 M-HO 1 (V{ M < z S 1^ s •H 0) 1 D ^ Q W Pi < 4J N tD P tt; M M P 2 a PS ' Q S D ^' Pd D ^ ' to mm Pu P g M K ft! 1 CQ ^ ri; rf; <: < tX •HXlrtl 9 O < 1 < o o o ^ D CQ I C/D 1 CQ 1 « 1 Qom 1 g. Q 2 J S s O 387 Abdullahpur where they play a negative role in increasing noise in these areas.

Similarly in Ghaziabad district, traffic is the major contributor of spreading noise in all the selected stations. Loudspeakers also generate noise in all the sample areas of Ghaziabad district including

Hapur, Dadri, Modinagar, Noida, Moradnagar, Loni and

Gharmukteshwar.

10.5.2.7 AIR BORNE DISEASES

Air pollution in Meerut and Ghaziabad districts through various sources gives rise to various related diseases that are affecting the health of the people.

The most common diseases that affect the health of the people in almost all the sample areas of Meerut district are eye - irritating, headache, nausea, bronchitis and asthama except in the areas of Mawana and Kharkhauda where bronchitis and asthama is not present (summary Table CVII). Skin diseases are visible in Abdullahpur, Mawana, Baraut, Baghpat and Kharkhauda while some other miscellaneous diseases are also common in Mawana and Daurala stations of Meerut district.

Similarly in Ghaziabad district, eye-irritation, headache and nausea are the main diseases that are 388

M u 0) iniooimiCTviooir-i i criicoit^iTriooivDiOio a) to iroicNiroiinir-iini 1 t^ir~it^ii-

01

CO OJ irornivci(Niinivoi ooii-iioiiniroioiroiin C CO itTvlCNliniOOllDfCOIVDI CNI^ICTllCNlChloOlinit"- •H (0 iCTllOOlf^OI'J'ltNllOlOl OOimiOOI'J' l «J3 1 O I in I fn M 0) ICrilV£>lCNiO>lOimit--l

1 it--icoicoiroir-i 1 uDiooiojioioiiooiini'j' e x: i«jii^icriimii»i

.tN.kDir~l«3.t~~iOin. O.n.VD.rO.HrO.tH.O cn (0 .cr>l00ir~irn.O.t~-.00l t--.CNIrH.tNlVDI'*lrH.iH H

iroiLn.r-it~-.cNiu3.n. r-icriixi.in ICri.OOir^.OOit^.iiDIt^. O.O.rH.fN.UJIM'linirH u .Ln.<3'iO'rHi(N)ivr)i(r.i r}<.vj3.init-H.rHiLnivoir- (0 lUJ.r-irN.tNi^f.Lniooi rH."T.cT\.i^.rH. ^~•..CT^.n .O.O.O.OiO.O.O. O.O.OIO.O.OlOlO l + . + l + . + l + l + ll. +. + . + ! + . + . + .. .+

icrii ..^icTiicTiir^ioo. ni«3<.tHi(N.'j'.r-ii%f.o x: in. .(TviONiCJ^lVDirOi O.O.(7\ltN.t^.[~.(Tl.r0 u iCTi.KqilTiicOlOOiOJrOl Oli-l.^.tNlCDlOO.O.'^ c icrv.M.cr.it^it-Hi[^.(ni o.vD.in.uj.in.Ch.nir^ 0 .Ol lO.OiO.O.O. OlOlO.O.OIOlO.O . + . l + . + l + . + ll. .. + . + ! + . + . + ....

C O •H iOO.l/1.V£.iCN.tN.O\.>3'. O.I~-.(N.'Xlim.OO.rOlO u .^.aO.'^.t^.rO.O.iH. CN.H.'^l'.^.^O.kDIrH.O 0) (0 .in.o.t^in.t~-.r-iit~-. o.n.t^.ooitNiooi^.rH ir-(iv£)iiri^iLni(Tiicrii u)i»3

1 1 i , 1 . . , t , . 1 . . S . Cd 1 . . 1 1 . 1 . 1 1 ... 1 X 4J u la p. -a . . .«. . i^.w •M 3 ^ U .Hqi

Noida. People of Babugarh, Moradnagar and

Garhmukteshwar are free from bronchitis while in

Babugarh, Hapur and Garhmukteshwar they do not suffer from skin diseases. Asthama, however, is positively- related in all the sampling stations except Babugarh.

Some other miscellaneous diseases also recorded a positive values in Hapur, Dadri, Modinagar, Loni and

Moradnagar areas of Ghaziabad district.

10.5.2.8 WATER BORNE DISEASES

Water pollution in the study area is an important item giving rise to many water borne diseases which affect people living in the study area. It is evident from the study Table CVIII that diarrhoea, jaundice, and dysentry are the main diseases in all the sampling areas of Meerut district except in Abdullahpur where dysentry plays negative role in affecting the health of the people. Some other diseases also damages health of the people in different sampling stations of the district. Among them, cholera comes out as the main water- borne disease in all the areas except in Daurala and Baghpat. Besides this, some other miscellaneous 390

M H tdvi'i • tint i<« to<-4 U E-

Q i'-tiOiOiiAt(Nt(Tviui< t£inir~-toiaoiu>tr' a M ((aiONiT-ft-.jit^tiniNi r»ir-i"*t'*iOi«'

X irnia)'U}trot^tcoto^iiffti'fiOiO\t {DlOl'Hl^^l* 1 . . . . . , . 1 . , . , . . . , . , . H lOiOtOiOtOiOiOi OtOiOiOiOiOtO'O H l-fl-fl + lllltlt + i 4-i)t + )4-l'«'l-*-lli +

n ta I > 1 < 1 i 1 1 •••III!

M ir»ifnooiooiwii«

Q Z iaoi<«'i(ni9t-ii ff4tmir«iooir^i

is < 1 ..... • .,.,.,.,...... < *j lOiOiOiOtOiOiO* OiO>00 t + i + i + r+i + i+i+t it + ,,i + ,+iii + .'*- H 13 Pi H H 2 1 . t t ...... 1 . t . . O '•'»'•< ' ......

«

a:a)i\ota3>o*^> en >l Ol t t 1 t » 1 * 1 1 1 . 1 1 . . 1 U UWim)U)'mtooi

H iHE-i'«>"iH.fcJi<7\i ff^lml(7^^t^.-^l^^.p-|* Hi . . 1 . . -z ...... m • OiOiOiO.Oi lOi O.OiOiOiOiO.O'O Pi • ll+l + t + l + l III >.4'. + * + il)..'*-i> O m I p; H X • 1 • 1 r 1 1 . i 1 . 1 . 1 1 a; 1 > t 1 1 t t t t 1 1 t . ) t H H •utiHi*ir«>ir'if«iiu)i H)u1l^o•n)Ul•w•vo'0^ Z >trHir<. ^.n.riintr-iOioiio ? U ir^ioivoioO'M*r-iO

p; Q I . . . 1 . , . 1 •...... ,.. o 'OiOtOiOiOiOiOi OiOiOiOtOiOiOiO

en CD sz;

H i< 1 • 1 • • 1 1 1 . ! . . 1 1 • K intHir^ieoimiOiHi inivoi(A<(nin'a)ir^|'~* H i«>(niOt-#i*(ni < »j tOii/iiinimiVviOi^i r>ir^iu)i<<*taoi*iHi-« »^ O 1 • . • 1 . . . 1 • 1 ...... i . 1 , . 1 . lOiOiOlOiOlOiOi OiOiOiOiOiOiO'O Pi • •t+ltl + l + tll + l 414.14. 4., + ! + O H U << I 1 1 t I 1 1 1 1 1 1 1 1 1 I u ioiroir>iOiiAiwi«i r« 0 iu>)aair'ioiuii<4*ir^( .-ii^i^iiniaoiotvifft X ••«iitAirt«BiOi«t tftio\tui«Ai«tt0i*«iir<.if^trniflB O < 1 . 1 • 1 • 1 • t .,.,... << M lOiOiOiOlOiQiOi 0-fiii4-t4i + t4-i-*- H

> 1 1 • t 1 I 1 > • 1 1 1 1 1 1 0£ 1 1 t 1 1 1 1 • . . i . . t < 1 1 .. 1 I 1 1 ..... t • 3 1 « II 'I U t 0 t • • i • 1^1 1 1 • 1 t t X * Vt U 1 0. 1 ) • 1 1 1 Q 1 t) • 1 • K 1 1 1 rC t M •HiJiXi 1 I i».<. i < * •z>H>< < lOi • * 0< ' yi UM.J.<<.J.H.Kr.<.X..H«^i . •.<) 1 tZiD a«>a)2it3>''tJH9i'DiO:iHtMiQiiDiB:iK>o><<>aQizitHio:ia£

•'X).-3

Baraut and Sardhana. Throat -infection is also found in

Abdullahpur, Mawana, Daurala, Baghpat and Kharkhauda stations of Meerut district. Typhoid is common mainly, in Abdullahpur, Mawana, Daurala and Kharkhauda but other sample stations remain free from its impact.

In Ghaziabad district, dysentry and diarrhoea are revealed as the main water related diseases in all the sampling areas except in Dadri. Typhoid is the second main water related disease of all the sampling stations except in Hapur and Moradnagar. Cholera is the important disease that is positively related to

Babugarh, Hapur, Dadri, Noida, Moradnagar and

Garhmukteshwar areas of Ghaziabad district. Presence of kidney stone is a problem in few areas of Hapur,

Dadri, Modinagar and Moradnagar. People residing in

Babugarh, Hapur and Moradnagar complain about the throat - infection while in other areas of Hapur,

Modinagar, Loni, Moradnagar and Garhmukteshwar people suffer from jaundice which is the out come of water pollution in Ghaziabad district. CHAPTER XI 392

SUGGESTIONS

The analysis conducted earlier has projected the

fact that maintenance of purity and safety of the

environment in the face of increasing urbanisation,

industrialisation and mechanisation of daily life is a most challenging task. In the interest of the present

and future generation, necessary steps should be undertaken for sustainable use of land, its mineral and water resources, plants and animals to preserve the purity of air, water and ensure reproduction of natural wealth and improve the quality of environment.

Industries creates pollution everyday in the form of increase in smoke, noise, heat, gas and fumes.

Industries also cause land pollution or dumping of solid wastes in open areas which get leached into the soil and pollute the soil as well as the ground water.

The situation may be retrived by adopting pollution control measures through installation of relevant devices. The cost of pollution control devices is high but the social cost of pollution is more significant and should be taken care of. The society suffers from damaging effects of pollution in the form of poor 393 health and associated reduction in productivity of people and the quality of life, the strain on medical services, degradation of land, corrosion of buildings and damage to flora and fauna. These cost are not only inevitable but much higher than for installing pollution control technology. With very poor environmental controls being exercised by the authorities many air and water polluting industries are set up near urban areas. The pollution control need to be implemented strictly by the concerned authorities.

The nature and quality of wastes differ from industry to industry depending upon the nature of raw materials and process used and product manufactured.

The water discharge from most of the industries are contaminated and often unfit for irrigation. Most industries discharge waste water into rivers and water courses without adequate treatment. Industrial effluents are not easily biodegradable and beyond the capacity of natural assimilation by the rivers, with the result that water bodies remain polluted affecting the health of the people in the region. Water-borne diseases create a major problem in every monsoon when 394 water logging particularly, in the low income settlements causes contamination of water leading to a variety of water-borne ailments. Cholera, dysentry and gastroentritis claim many lives every year. Besides these, foul smell emanating from open drains is unbearable and the water in them creates an unpleasant sight. People of the poorer sections of the society are forced to use this water for washing and bathing leading to various types of skin diseases. Proper collection and disposal of liquid or solid wastes is very important for the overall health of the people.

The awareness for disposal of hazardous waste is yet to pick up amongst industrialists and civic authorities.

However, it is presumed that industry would remain at variance with the environment and little effort is made in harmonising the two. This can be achieved if the industries adopted the following measures.

The concept of prevention of pollution should be right from the time of introduction of process technologies and selection of raw materials.

Recycling of effluents is very important. This technology is now acknowledged world over in attaining better results in pollution control. A necessary evil 395 of most forms of development is generation of wastes and residues. If non-biodegradable they pose a major health hazards once these affect the life support system and enter the food chain. However, wastes and residues can be reused to a substantial degree.

Recycling technology is now used in ataining tangible results in pollution control.

In properly selected process of any plant, effluent treatment is rendered a paying preposition.

The costs of recovery of raw materials, intermediate products and final products outweigh the cost of effluent treatment. This has been practically exhibited in industries manufacturing vegetable oils, caustic soda and bleaching powder.

Use of bio-technology has revolutionised effluent treatment all over the world. Plants, animals and birds are interconnected and depend upon each other directly or indirectly and make biological community, where survival of one is dependent upon survival of others.

Optimum use of micro-organisms splits up organic matter in the effluent. This has become the crux of the biological treatment process as adopted in industries. 396

The discharge of pollutants in the form gases

liquids or solids should be strictly controlled. Limits

for discharge of pollutants or gases from the

industries have been imposed by the pollution control

boards for majority of industries but implementation of

law is the main problem and should be looked into

carefully.

Water used by industries is discharged to the land

or water bodies like rivers or ponds. It can

contaminated, alter or deteriorate the quality of fresh

water. The industrial effluents discharge should be of

such quality that it does not cause pollution. Thus,

all industries should have an effluent treatment and

control system judiciously operated and designed to

render effluent quality that meet the tolerance limit

for industrial effluents set by pollution control

boards.

To sum up, industrial pollution can be controlled by

Selecting site based upon detailed environmental

impact assesment.

Incorporation of control measures at project

planning stage. 397

3 . Incorporation of proper processess to eliminate or

reduce emission of wastes.

4. Incorporation of treatment methods for liquid and

gaseous emissions.

5. Continuous monitoring and management for

environmental protection.

Pollution from industries can be controlld by adopting various well tried pollution abatement technologies. The government machinery can play a powerful role in enforcing pollution control measures.

The United Nations conference on 'Human Environment' in

1972 and 'Rio Summit in 1992' have focused to worsening global environment. The decision of the conference were understood and accepted by the Government of India in true spirit which is witnessed by her consequential efforts made in the field of environment. Legal measures to protect and improve the environment have gradually crystalised into an evolving body of

'Environmental Law'. Increasing thrust is now being given to environmental policies and specialised environmental status.

In November 1980, the Government of India set up a 398 nodal 'Department of Environment' and later on Ministry of Environment and Forests was formed. Parliament was empowered to enact laws relating to air, water, noise and sea pollution while state legislation were also allowed to enact laws for regulating and monitoring different types of pollution but with limited jurisdiction.

These legislations enacted by the Parliament in this regard were

The Air (Prevention and Control of Pollution) Act, 1974

The Water (Prevention and Control of Pollution) Act,

1981

The Forests (Conservation) Act 1980 he Environment (Protection) Act 1986

The Motor (Vehicles) Act 1988

Central Acts for Protection of Envimment

Government of India has enacted several laws for the protection of forests and environment and for the prevention of air and water pollution and there are also proposals to enact more laws to deal with environmental problems more effectively.

The Wild Life (Protection) Act, 1972

This Act provides for the protection of wild 399 animals and birds and for matters connected. The Act envisages, the appointment of Director of Wild life preservation by the central Government and chief wild life warden by the state Government and the constitution of a wild life Advisory board. The Act also provides notification of 'Sanctuaries', 'National

Parks',' Game Reserves' and 'Closed Areas' by the State

Government.

The Water (Prevention and control of Pollution) Act,

1974

This law was enacted in pursceance of clause (1) of Article 252 of the constitution of India to provide for the prevention and control of water pollution and the maintenance or restoration of wholesomeness of water. The purpose of this Act is to ensure that the rivers, streams and other sources of drinking water and water for support of fish life and for use in irrigation are not allowed to be polluted by the discharge of domestic and industrial effluents. The Act envisages establishment of a central board for the

Prevention and control of Water Pollution and also

State boards to deal effectively with the problem of 400 water pollution in the country and provides penalties for contravention of the provisions of the Act. The Act also provides for setting up of central and State water testing laboratories to enable the boards to assess the extent of pollution and lay down the standards. The Act was amended in 1978 to remove certain practical difficulties faced in its implementation. It was further amended in 1988 renaming the boards as

Central/State Pollution Control Boards so that they may deal with both water and air pollution control. The

Central Board was empowered to perform the functions of the State Board in centain situations and penal provisions were made strict. Boards were given powers to give directions including direction for closure or stoppage of water and electricity supply and other services to the offending establishments. Obtaining consert of the board was made obligatory at the time of establishing an industrial unit.

The Forest (conservation) Act, 1980

The purpose of this Act is to check indiscriminate dereservation and diversion of forest land for non forest purposes. The State governments are required to submit formal proposals for declaration of reserved 401 forest as dereserved and for diversion of forest land for non- forest purposes to the Ministry of Environment and Forests for approval.

The Air (Prevention and control of Pollution) Act, 1981

This law has been enacted in pursuance of the decision taken in the U.N. Conference on Human

Environment held in Stockholm in June 1972. Appropriate steps would be taken for the preservation of the natural resources of the earth which among other things, include the preservation of the quality of air and control of air pollution. The pollutants present in the air beyond a certain limit, discharge through industrial emissions and from certain human activities connected with traffic , heating , use of domestic fuel, refuse and incineration has a detrimental effect on the health of the people as well as animal life, vegetation and property. The Act envisages an integrated approach for tackling such problems. It provides that the central and State boards set up for the preservation and control of water pollution under the Water ( Prevention and contnrol of Pollution ) Act,

1974 shall perform the functions in respect of 402 prevention control and abatement of air pollution.

The Act was amended in 1987 to make its implementation more effective. In fact, the amendments made in this Act in 1987 were substantially incorporated in the Water (Prevention and control of

Pollution) Act in 1988.

The Environment ( Protection ) Act 1986

This is a general legislation on environmental protection should enable coordination of activities of various regulatory agencies, creation of an authority or authorities which adequate powers for environmental protection, regulation of discharge of environmental pollutants and handling of hazardous substances, speedy response in the event of •accidents threatening environment and deterrent punishment to those who endanger human environment, safety and health. The Act enpowers the central Government to take all such measures as it deems necessary or expedient for the purpose of protecting and improving the quality of environment and preventing, controlling and abating environmental pollution.

The Ministry of Environment & Forests has taken several measures for implementation of the provision of 403 this Act including framing of rules, notification of standards and environmental laboratories, identification .of agencies for hazardous chemicals management and setting up of Environmental Protection

Council in the states.

The Water ( Prevention and control of polltion ) Cess

Act 1977

This law was enacted to provide for levy and collection of axcess on water consumed by persons earring on industries and by local authorities with a view to augmenting the resources of the Central

Pollution Control Board and the State Pollution Control

Boards for the prevention and control of water pollution constituted under Water/Prevention and control of Pollution ) Act, 1974.

The Act is being amended with a view to augmenting the resources of the Pollution Control Boards by removing the lacunae in the Act and to provide rebate to the industries for complying with the consumption and effluent quality standards.

Central Pollution Control Board was set up as national apex body for the assessment and control of 404 water and air pollution. The central board co-ordinates the activites of 18 state Pollution control boards. The central board initiated preparation of comprehensive industry documents for some specific types of industries. On the basis of documentation, Minimal

National Standards for specific types of industry were evolved and nation wide implementation of pollution control in these industries is being vigirously pursued. The Department of Environment has also set up

'Envornmental Impact Assesment Centre' Education and

Training Centre, Eco-Development Board and National

Conservation Strategy Centre .

Indian Penal code mentions various laws which concern environment. These are some specific Acts that help in protecting the environment, e.g. The Factories

Act 1948 , Insecticide Act 1960 and Motor Vehicles Act

1939. In addition to these, several State governments have enacted special laws which can be evoked for protecting and improving invironment. The Act mandates that no person carrying any industry, process or operation shall dischare or emit or permit to discharge any environmental pollutants in exess of permissible standard limit. Thus, all persons directly or 405 indirectly responsible for the offence by their actions/ ommision or negligence are liable for punishment under the Act.

The government is aware of the problem and has formulated various laws to punish those involved in polluting environment. Laws, however, remain useless on paper if they are not enforced properly. The first thing in this regard is to see that they are forcefully implemented and secondly the public in general is required to cooperate and respect to authorities if there is laxity in any quarter. Public should also be educated about the ill effects of uncontrolled environmental exploitation so that they can willfully help in restoring the ecological balence. 406 SELECTED BIBLIOGRAPHY

Books

Ajmal/ M. and Raziuddin., Studies on the pollution of Hindon and Kalinadi", in Trivedy, R.K.(ed.), Ecology' and Pollution of Indian River. New Delhi, 1988.

Anand, K.V., "Growth of small scale industries in U.P."; Problem and Prospects," in Tiwari, T.R. and Joshi, A., (ed.) Development and change in India. Ashish Publishing House, New Delhi; 1988

Back, W., Atmospheric Pollution. Mac-Graw Hill Book Company, U.S.A., 1972. jBarins, M.S. and Bajwa, G.S., "Air Pollution and its legal control", in Sapru, R.K. (ed.) Environmental Management in India. Vol.11, New Delhi, 1987.

Bairoch, P., The Economic development of the Third World Since 1900. Methuen and Company Ltd., London, 1975.

Berry, B.J.L., Urban Environmental Management.- New Jersy, 1974.

Berry, H.A., Environmental Hazards in British Isles. London, 1977.

Benjamin, K.H.S., (ed.). Dimension of Environment. With reference to condition in India. Centre for Human Development and Social change, Madras, 1982.

Blanford, H.F., Climate and Weather of India. Ceylon and Burma. London, 1989.

Chattopadhyay, B.S., "Problems of Environmental Pollution in Rural Areas with Reference to Agriculture and Health", in Ray Chaudhary, S.R. (ed.) Environmental Pollution and Toxicology; New Delhi, 1987 407

Cherry, E.G., Urban Planning Problems. Leonard Hill Company, London, 1974.

Fisher, C.A., Resource and En vi r onmen t a 1 Economics, Cambridge University Press, London, 1984.

Hinkle, E.L. and Loring C.W., The effect of the Man- Made-Environment on Health and Behaviour. castle House Publication Ltd., London, 1979.

Kayastha S.L. and Kumra, V.K., Environmental Studies ; fundamentals Problems and Management. Tara book Agency, Varanasi, 1986.

Khoshoo, T.N., Environmental Concern and Strategies. New Delhi, 1988

Krishan, M.S., Geology of India and Burma. Madras, 1956.

Kudesia, V.P., Air Pollution. Pragati Prakashan, Meerut, 1986.

Kumar, H.D., Modern Concept of Ecology. New Delhi, 1977.

Mahajan, G., "Effects of Water Pollution on Health", in Kumar, R., (ed.). Environmental Pollution and Health Hazards in India. New Delhi, 1987.

Mahajan, V.S., Indian Economy and Regional Development. Deep Publication, New Delhi, 1982.

Maurya, S.D., Urban Environmental Management. Chug Publication, New Delhi, 1988.

Meethan, A.R., Atmospheric Pollution Pergaman Press, London, 1964.

Menarsia, R., Environmental Conservation and Planning. Ashish Publishing House, New Delhi, 1989.

Pathak, H. , "Environmental Management in India", in Sapru R.K., (ed.), Environmal Management in India. Vol.1, New Delhi, 1987. 408 Ray, Chaudhary, Agarwal, S.P., Soils of India. Indian council of Agricultural Research, 1963, New Delhi.

Ray, S. K., Economics of Development. New Delhi, 1988.

Sati, N.D., Environmental Design and Development; conflict and Harmony. Jodhpur, 1987.

Sapru, R.K., (ed.). Environmental Management in India. Ashish Publishing House, New Delhi, 1987.

Singh, Bali, Ram., Studies in Environment and Development. Common Wealth Publisher, New Delhi, 1988.

Saxena, K.D., Environmental Planning. Policies and Programmes in India. Shipra Publications, Delhi, 1993.

Singh, H.P., Resource Appraisal and Planning in India•• A case study of backward region. Rajesh Publications, New Delhi, 1979.

Spate, O.H.K., India and Pakistan. London, 1957.

Sxuidaram, K.V., Urban and Regional Planning in India, Vikas Publishing House, New Delhi, 1977.

Verma, S.S., Urbanisation and Regional Development in India. Chug Publication, Allahabad, 1989.

Wadia, D.N., Geology of India. New Delhi.

Watts, H.D., Industrial Geography, New york, 1987.

Zelinsky, W., Geography of a Crowding World. Oxford University Press, U.S.A., 1970.

Zimmerman, E.W., World Resources and Industries New York, 1951. 409 JOURNALS '"^ Atimad, Nazeer., "Sugar in India, "The Geographer. March, 1927.

Basu, Biman., "Environmental Protection; A many faceted Problem", YOJANA. Vol 30, No.10, June 1-15, 1986.

Basu, Biman., "Twin threat to our environment", YOJANA. Vol 32, No.10, June 1-15, 1988.

Bagehi, Kanagopal., "Environmental Planning : An Ecological Approach", The Geographical Review of India. Vol 47, No.3, September 1985.

Behl, R.K., "Geography of Water and Air Pollution", YOJANA. Vol.29, No.24, June 1-15, 1987.

Cbaudhary, N., "And How to clean Ganga", YOJANA. Vol 29, No. 10, June 1986.

Gautam, A., "Supply Area and Output Characteristics of a Sugar Mill : A case study of Mawana Sugar Works", The Geographical Observer. Vol 15, 1979.

Hussain, Irshad and Siddiqi, N.A., Urban Encroachment on Rural Lands : A case study of Ghaziabad city", The Geocrrapher. Vol 24, No.2, 1977.

Hussain, M. , "Agricultural Land-use in Meerut district", The Geographical Observer. Vol 15, 1969.

Kumar, D., "Ecosystem Approach for Sustainable Economic Development", Indian Journal of Regional Science. Vol 20, No.l, 1988.

Prakash, B., "Location and Movement of Handloom cloth Industry with in the Meerut Town", The Geographical Observer. Vol 5, March 1969.

Kumra, V.K., "Environmental Pollution and the human Health", The National Geographical JOURNAL of INDIA. Vol 26, Part. I and II, 1980. 410 Prakash, M., "Levels of Industrial Development in India", The Geographical Outlook. Vol 15, 1978.

Pratap, R., "Water Pollution in Bihar", The Geographical Review of India, Vol 47, No. 4, 1985.

Rasul, S.H., "Case for Vigorous Environmental Education and Awareness in Developing countries", The Geographer. Vol 27, No.2, 1980.

Singh, A., "Location of Sugar Industry in the National Capital Region", The Geographical Observer. Vol 16, 1980.

Singh, L. , "Urban Dynamics and Land-use Transformation; case study of Ghaziabad", Town Planner Journal. Vol 9, No.3, 19 91.

Singh, R. and Shukla, L., "Spatial Distribution of the Incidence of Trachoma in Jaipur, "The Geographer. Vol XXXV, No.2, 1988.

Singh, R.L., "Ecology of Urban Habitat and Environmental Planning in Indi.a", The National Geographical. Journal of India, Vol 31, Part 4, December 1985.

Stoddart, R.S., "Our Environment", Area, Vol.2, No.l, 1970.

Talha, M., "Bringing Stability to Sugar Industry", YOJANA. Vol 31, No.11, 1987.

Trewartha, G.T., "A case for Population Geography", Annals for the Association of American Geographers. Vol XLIII, No.2, June 1953. APPENDIX - A 411 QUESTIONNAIRE

HABITAT QUALITY

1. Extent of over crowding in the area.

2. Extent of foul smell in the area.

3. Extent of fumes/smoke.

4. Extent of garbage found in heaps.

5. Extent of garbage spread everywhere.

6. Extent of flooding of drains.

AIR POLLUTION

1. Extent of air pollution due to wood burning.

2. Extent of air pollution due to waste disposal.

3. Extent of air pollution due to Kerosene burning.

4. Extent of air pollution due to dead body burning.

5. Extent of air pollution due to vehicles.

WATER POLLUTION

1. Extent of water pollution due to waste water from

houses.

2. Extent of pollution due to septic tanks/soak pits.

3. Extent of water pollution due to industrial

pollutants.

4. Extent of water pollution due to dairy animals.

5. Extent of water pollution due to water logging. 412 NOISE P0LLX7TI0N

1. Extent of noise pollution due to vehicular

traffic.

2. Extent of noise pollution due to loudspeakers.

3. Extent of noise pollution due to industrial

operations.

LAND DEGRADATION

1. Extent of land degradation due to domestic refuse.

2. Extent of land degradation due to industrial

refuse.

3. Extent of land degradation due to brick bhattas.

4. Extent of garbage dumped on municipal collection

sites .

5. Extent of garbage collected from the streets.

6. Extent of garbage collected once a week.

7. Extent of garbage collected twice a month.

8. Extent of garbage collected once a month.

9. Extent of disposal of garbage on the street.

10. Extent of disposal of garbage in the drain.

QUALITY OF LIFE

1. Extent of migration in degrading quality of life.

2. Extent of congestion/lack of open space in degrading quality of life. 413

3. Extent of absence of suitable schools in degrading

quality of life.

4. Extent of low income group people in degrading

quality of life.

5. Extent of unemployment in degrading quality of

life.

6. Extent of lack of health facilities in degrading

quality of life.

7. Extent of shortage of electricity in degrading

quality of life.

8. Extent of shortage of water supply in degrading

quality of life.

COMMON DISEASES

WATER-BORNE DISEASES

1. Diarrhoea

2. Cholera

3. Dysentry

4. Kidneystones

5. Throat infection

6. Jaundice

7. Typhoid

8. Other diseases 414 AIR BORNE DISEASES ^'•^

1. Eye-irritation

2. Bronchitis

3. Headache

4. Nausea

5. Asthma

6. Skin diseases

7. Other diseases