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GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) PRE-FEASIBILTY REPORT FOR EXISTING KHADSALIYA LIGNITE MINE (Regarding Validation of Environmental Clearance Under the provision of EIA Notification 2006 and in compliance of MoEF & CC Notification Dated 06 th April 2018) V LLAGE KHADSALIYA TALUKA BHAVNAGAR DISTRICT BHAVNAGAR GUJARAT Capacity 0.40 MTPA Lease Area 171.0 Hectare

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Page 1: GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) · GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) PRE -FEAS IBILTY REPORT FOR EXISTING KHADSALIYA LIGNITE MINE (Regarding Validation of

GUJARAT HEAVY CHEMICALS LIMITED,

(GHCL Ltd.)

PRE-FEASIBILTY REPORT FOR

EXISTING

KHADSALIYA LIGNITE MINE

(Regarding Validation of Environmental Clearance Under the provision

of EIA Notification 2006 and in compliance of MoEF & CC Notification

Dated 06th April

2018)

V LLAGE KHADSALIYA

TALUKA BHAVNAGAR

DISTRICT BHAVNAGAR GUJARAT

Capacity 0.40 MTPA

Lease Area 171.0 Hectare

Page 2: GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) · GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) PRE -FEAS IBILTY REPORT FOR EXISTING KHADSALIYA LIGNITE MINE (Regarding Validation of

CONTENTS

Description Page No.

1.0 BACKDROP 1

2.0 LEASE DETAILS & STATUTORY CLEARANCES 1

2.1 PRESENT STATUS 2

3.0 BRIEF HISTORY OF MINING IN KHADSALIYA VILLAGE 3

4.0 PROJECT AND ITS OBJECTIVE 3

5.0 PROJECT SITE INFORMATION 5

5.1 TOPOSHEET NO WITH LATITUDE AND LONGITUDE 5

6.0 IMPORTANT SURFACE FEATURES 5

7.0 PHYSIOGRAPHY AND DRAINAGE 6

7.1 PHYSIOGRAPHY 6

7.2 DRAINAGE PATTERN AND NATURAL WATER COURSE 6

8.0 CLIMATE AND VEGETATION 6

8.1 CLIMATE 6

8.2 VEGETATION 8

9.0 CURRENT LAND USE PATTERN 8

10.0 REGIONAL GEOLOGY 8

10.1 General Description of the Formations 8

10.1.1 Deccan traps 9

10.1.2 ALTERED BASALT 9

10.1.3 SUPAA TRAPEAN 9

10.1.4 KHADSALIYA CLAY 9

10.1.5 GAJ FORMATION 10

10.1.6 LAKHANKA FORMATION 10

11.0 LOCAL GEOLOGY 10

11.1 LIGNITE OF THE BASIN 12

11.2 SUB SURFACE STRATIGRAPHY 12

11.3 STRUCTURE 12

12.0 DESCRIPTION OF MINERALS 12

12.1 Lignite 12

12.1.1 Lignite seams 13

12.1.2 Mineable lignite seams 14

12.2 Overburden 14

Page 3: GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) · GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) PRE -FEAS IBILTY REPORT FOR EXISTING KHADSALIYA LIGNITE MINE (Regarding Validation of

12.2.1 Distribution of overburden strata 15

12.3 Soil 15

12.4 Sand 15

12.5 Clay 16

12.6 Inter burden 16

13.0 RESERVE 16

13.1 Lignite Reserves 16

13.2 Mineable Lignite 17

14.0 EXPLORATION DATA 17

14.1 CGM REPORT 17

15.0 RESERVE ESTIMATE 18

15.1 NORMS FOR MINEABILITY 19

15.2 RESERVE ESTIMATION BY THICKNESS CONTURE METHOD 20

16.0 GEOLOGICAL RESERVES AND GRADE 21

16.1 Lignite Reserves and Occurrences 21

17.0 QUALITY OF LIGNITE 22

17.1 Petrography of Lignite 22

17.2 Chemical Composition 22

18.0 TRANSPORT SYSTEM 23

18.1 Transportation of Men and Material 23

19.0 WATER PUMPING AND DRAINAGE SYSTEM 23

19.1 Surface Water 23

19.2 Ground Water 23

20.0 METHOD OF WORKING 24

20.1 Method of Mining 24

20.2 BENCH GEOMETRY 24

20.3 QUANTUM OF LIGNITE PRODUCTION AND OB 25

20.4 Supporting Composite Plan 26

20.5 Rate of Lignite Production and Life of the Mine 26

20.6 SUPPORTING COMPOSITE PLAN 27

21.0 INFRASTRUCTURAL FACILITY 29

21.1 Site Services 29

21.2 CONSTRUCTION OF WEIGH BRIDGE 29

Page 4: GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) · GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) PRE -FEAS IBILTY REPORT FOR EXISTING KHADSALIYA LIGNITE MINE (Regarding Validation of

21.3 SUPPLY OF ELECTRIC POWER 30

21.4 SUPPLY OF DRINGKING WATER 30

21.5 TRANSPORTATION OF MEN AND MATERIAL 30

21.6 COMMUNICATION SYSTEM 30

21.7 MEDICAL FACILITIES 30

21.8 EMPLOYMENT POTENTIAL 30

22.0 CAPITAL COST ESTIMATE 31

23.0 ENVIRONMENTAL MANAGEMENT PLAN 31

23.1 ENVIRONMENT PROTECTION COST 32

23.2 AMOUNT OF CSR ACTIVITY CONTRIBUTION 33

24.0 BASELINE INFORMATION 34

24.1 EXISTING LAND USE PATTERN 34

24.2 WATER REGIME 34

24.3 CLIMATIC CONDITION 35

24.4 FLORA AND FAUNA 35

24.5 HUMAN SETTALMENTS 35

24.6 QUALITY OF AIR AND WATER 35

24.7 WHETHER THE AREA FALLS UNDER NOTIFIED AREA 38

24.8 CROPPING PATTERN 38

24.9 EXISTING OF NATIONAL PARK 38

25.0 ENVIRONMENTAL IMPACT ASSESSMENT 38

26.0 ENVIRONMENTAL MONITORING 39

26.1 Air Environment 39

26.2 Water Environment 39

26.3 Noise Environment 39

26.4 Land Environment / Land Use Planning 39

27.0 MEASURE FOR DUST SUPPRESSION 42

27.1 Measures to Minimize Vibration Due To Blasting And Check Noise

Pollution 43

28.0 AFFORESTATION PROGRAMME 43

28.1 Stabilization and Vegetation of Dumps 43

28.1.1 Proposed dumping area 44

28.1.2 Old dumps 44

Page 5: GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) · GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) PRE -FEAS IBILTY REPORT FOR EXISTING KHADSALIYA LIGNITE MINE (Regarding Validation of

28.1.3 Inside Dump yard 45

29.0 MEASURES FOR MINIMIZING ADVERSE EFFECT ON WATER

REGIME

45

29.1 Treatment and Disposal of Water from the Mine 45

29.2 Measures to Minimizing Adverse Effect on Water Regime 45

29.2.1 GROUND WATER 45

29.3 Socio-Economic Environment 45

29.4 Ecologically Fragile Area 46

29.5 Conceptual Mining Plan 46

29.6 Disaster Management Plan 46

Page 6: GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) · GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) PRE -FEAS IBILTY REPORT FOR EXISTING KHADSALIYA LIGNITE MINE (Regarding Validation of

1.0 BACKDROP

The development of a nation depends on industrial and agricultural growth. The

Post-independence era has witness Comprehensive industrialization in our country.

The importance of lignite in industrialization of Gujarat was forecasted as early as

1946 by Venkatappaiah, a Geologist of the Geological Survey of India

(GSI). The drilling to establish Lignite deposit in this Lakhanka-Khadsaliya Block

was done by Directorate of Mining and Geology, Govt. of Gujarat.

GHCL is allotted a captive Mining Lease for Lignite extending to 171.0 ha area at

VILLAGE Khadsaliya in Bhavnagar district to use lignite at its own chemical & power

Plant at V. Sutrapada. The area was initially explored by the State Dept. of Geology

& Mines (now Commissionerate of Geology & Mines).

In order to meet the requirement of their existing captive thermal power plant and its

expansion on a sustained long term basis GHCL had drawn up plans to open a new

lignite mine in Bhavnagar district at Khadsaliya .

2.0 LEASE DETAILS & STATUTORY CLEARANCES:

Following statutory clearances / approvals are received from different authorities:

i) Lignite block allotment: No. 47011/23/99-CPM Govt. of India ministry of mines and minerals, department of coal, New Delhi 4th April 2000.

ii) Approval of Mining Plan : Vide MoC letter no. 4024/4/97-Lig dated 23rd

Jan 2001 for annual production capacity of 0.4 million Tonne

iii) Environmental Clearance : Ministry of Environment & Forest vide its

letter no. J.11015/28/2002-IA.II(M) dated 7th October 2003

iv) Grant of ML by State Govt .: Vide GoG order No. MCR-1097-3052 (Part-

II)-CHH-I dated 24th June 2002

v) NOC from GPCB : Vide letter No. PC/NOC/BHV-

1

Page 7: GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) · GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) PRE -FEAS IBILTY REPORT FOR EXISTING KHADSALIYA LIGNITE MINE (Regarding Validation of

657/26763 dated 30/8/2001 vi) Permission from DGMS : DMS Udaipur letter No. UR/3315 dated 10-7-2007, renewed vide letter no. Ur/984 dated 19-2-2009, under Reg. 98

(1), 98 (3) under CMR 1957, without deep-hole blasting.

vii) Consent from GPCB : Consent vide Order No. AWH-96604

ix) Mine Closure Plan approved vide No. 48024/4/1997-Lig/CA-1 dated 3rd June

2016

2.1

PRESENTSTATUS

Now the applicant seeking for validity of the environmental clearance

as per provisions of EIA Notification, 2006 and recent notification of

MOEF&CC, New Delhi (S.O. 1530 (E) notification dated 6th April, 2018.

The mine is located at Village Khadsaliya, Taluka Bhavnagar, District Bhavnagar

Gujarat, having following Private and Government Khasara Nos. as given below:

LIST OF PRIVATE SURVEY NOS. OF VILLAGE “KHADSALIYA” FOR THE

LEASE

S.

No.

Village Survey No. Area in hect. Owners Name Remark

01 Khadsaliya 410/P 128.73.29 GOVERNMENT

02 59/p,60,62,3

6/1,63/2,64,

65,377,397,

398,399,400

42.26.71 PRIVATE

Grand Total 171.00.00

2

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3.0 BRIEF HISTORY OF MINING IN KHADSALIY

VILLAGE

The Block /Mining lease is located about 35 Km south east of Bhavnagar city in

Bhavnagar Taluka and is well connected by all-weather roads from North of the

area to Bhavnagar via Ghogha and Koliyak

4.0 PROJECT AND ITS OBJECTIVE

This is existing lignite mine having mining lease area 171.00 Ha with

production capacity 0.40 MTPA for environmental clearance for Mining is

already granted for the lignite mining vide latter No. J.11015/28/2002-IA.II(M)

3

Page 9: GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) · GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) PRE -FEAS IBILTY REPORT FOR EXISTING KHADSALIYA LIGNITE MINE (Regarding Validation of

dated 7th October 2003 having production capacity of 4,00,000 TPA in 171.0 ha.

Area.

4

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5.0 PROJECT SITE INFORMATION

The Khadsaliya Lignite deposit is at a distance of 35 km from Bhavnagar, The

area is well connected by all-weather roads. From the North the area is accessible

via Bhavnagar, Ghogha, and Koliyak. From the south the area has connected road

via Talaja, Tansa, & Morchand.

The nearest railhead is at a distance of about 35 Km from Bhavnagar.

5.1 Toposheet No. with latitude and longitude

The mining lease area falls in survey of India Toposheet No. 46C/2. Aerial distance

for site to SH 37 (Ghogha-Tansa) on west is about 5 Km. Gulf of Khambat is

almost 3 km on east side. The Location plan is shown in Fig. the Block with area

171 Ha allocated to GHCL falls in Survey of India Toposheet No. 46 C/2 within the

following coordinates:

Longitude 720 13’ 47” to 720 14’ 41”

Latitude 210 33’ 29” to 210 34’ 38”

6.0 IMPORTANT SURFACE FEATURES

The prominent physiographic features like the drainage pattern

(natural water courses/rivers), roads, location of villages are shown in the plan.

The area is generally characterized by flat to moderately undulating landscape

and the topography is gently sloping towards North and South.

The elevation of the area ranges from 66 m in the NW corner to 27 m. in S.E. the

area is mainly drained by Ramdasia River, South of the Mining Lease area,

flowing from West to East and into Gulf of Cambay.

5

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7.0 PHYSIOGRAPHY AND DRAINAGE

7.1

Physiography

The area falls on the Survey of India Toposheet No.46 C/2. The area is generally

characterized by flat to moderately undulating landscape and the topography is

gently sloping towards East & South East. The surface cover Alluvium, Coastal

dunes, mud flats and beach sands.

The elevation of the area ranges from 66m in the NW corner to 27 M in S.E. the

area is mainly drained by Ramdasia River, south of the mining Lease area following

from West to East and into Gulf of Cambay.

7.2 Drainage Pattern and Natural Water Course

There are no perennial river or major surface water bodies within the proposed

lignite field or mining lease area. The only river which is of significance is

Ramdasia River passing out side of mining lease area which flows from West to

East side and is entering Gulf of Cambay.

However this is a seasonal river and is dry most of the period except during

Monsoon, A canal (Shetrunjay is passing besides the lease area and flows from

South to North side.

8.0 CLIMATE AND VEGETATION

8.1

Climate

The characteristic feature of the climate are very hot summer and very low rainfall

during monsoon. In general, the year can be divided into three seasons

� Monsoon season, lasting from Late June to October

� Winter season , lasting from November to February

� Summer season, lasting from March to June.

The rainy period is hot and humid. Most of vegetative growth occur during

monsoon. The post monsoon period is again hotter with very high day temperature.

Usually, most of the vegetation dries out during this periods. Winter is mild and last

6

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about three to three and half months. During this season the standing dry plants

also disappear and the ground looks almost barren. The summer is too dry and hot,

May being the hottest month. Wind are strong during summer and monsoon

seasons. The relative humidity reaches over 94% during monsoon and the rest of

the year is comparatively dry.

Year Rainfall in mm

1979 888.30

1980 461.50

1981 704.20

1982 251.6

1983 844.1

1984 536.7

1985 677.5

1986 317.5

1977 179.3

1988 655.6

1989 557.8

1990 857.6

1991 436.7

1992 694.6

1993 434.2

1994 751.5

7

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8.2 Vegetation

Khadsaliya Lignite mining lease, most of the area is govt. waste land the

agriculture is limited to private land only. The plantation is only confined to

old/inactive dumps on the eastern periphery near mines office/Administrative

office on the South part of the Khadsaliya lignite mine lease, Desi Baval,

Bamboo, Gulmohar, Neem, trees etc. were planted in these areas. Mine-sump

Water is routed through clay lined pond(s) at surface where lime treatment is given

to neutralize the effect of Sulphur /pyrites. The entire water is used for dust

suppression, plantation and other miscellaneous use within mining area.

9.0 CURRENT LAND USE PATTERN

The initial land use pattern before mining operation was as follows:

Land type Private Govt. Goucher Total

Area in Hect. 42.2671 128.7329 171.0.0

10.0 REGIONAL GEOLOGY

The geology of the mining area and Khadsaliya –Surkha blocks is part of the

Geology of Saurashtra Peninsula.

The Saurashtra Peninsula is bounded by Sea on all sides except on the North-

East where it is flanked by alluvial plains and formation ranging from

Jurocretaceous to recent coastal deposits.

The area under consideration predominantly exposes geological sediments that

were deposited on the basement provided by Deccan Basalt.

10.1 General Description of the Formations

The area is mostly covered by alluvium, coastal dunes. The area under

consideration predominantly exposes geological sediments that were deposited

8

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on the basement provided by Deccan basalt. The geological formation based on

surface geological mapping and sub-surface lithological information of detailed

exploration, are as given. Such as Lakhanka formation (Agate conglomerate

formation), Gaj formation (Khadsaliya Clays) and Supratrapean Deccan trap.

10.1.1 Deccan traps

The rock is melanocratic in colour, hard compact and fine to medium grained

under microscope, it shows sub-ophitic texture. Plagioclase feldspar and

pyroxene are the main constituents.

10.1.2 Altered Basalt

The rock is gray in colour .It is soft and fine grained under microscope it

shows fine grained texture it is mainly consisted of laths and feldspar and

proxene.

10.1.3 Supra Trappean

The rock samples show shades of light gray and white. It is semi compact and

fine grained.

10.1.4 Khadsaliya Clay

I The rock is greenish grey/ash grey in colour. It is soft and fine-grained.

It is sticky by nature. At places, it contains microfossils. Under the

microscope. It shows extremely fine grained texture. On the basis of

colour R.I. birefrigerence, the sample mainly consists of ilite with

subordinate amount of kaolinite and montmorrillonite.

II Carbonaceous shale it is blackish in colour soft and fine grained. It soils

the finger. It contains lignite partings at places. It contains minute specks

of pyrite. It partially burns when ignited. And leaves behind some ash and

clays mass.

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10.1.5 Gaj Formation

Variegated Clay

It shows shades of yellow reddish, grey and white it is soft and fine grained. It is

sticky by nature. When dipped in water, it readily swells.

10.1.6 Lakhanka Formation

Conglomerate/sandstone

Most of the conglomerate and sandstone occurring in the area are loose and

friable in nature. The conglomerate is consisted of pebbles of chalcedony, agate,

quartz and sandstone. The sandstone is ferruginous hard and compact at places.

The sandstone and conglomerate wherever compact and hard can be used as

building stone.

11.0 LOCAL GEOLOGY

The Khadsaliya ML area predominantly exposes geological sediments that were

deposited on the basement provided by Deccan Basalt. The geological formations

are as given below:

Formations Lithology

Recent Alluvium, Coastal dunes and Beach sand, mud clays,

soil etc.

--------------------------------------- Unconformity ------------------------------------------------

Lakhanka Agate Conglomerate &

Formation (Agate Associated ferruginous

Conglomerate sandstone with intercalations

Formation) of clays. 9

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------------------------------------- Unconformity ------------------------------------------------

Gaj Formation Variegated sandstone, Marl,

Conglomerate and impure

Limestone, Gypsum Clays.

------------------------------------- Unconformity --------------------------------------------

Khadsaliya Gray to greenish gray clays

Clays With carbonaceous clay and lignite

With siderite nodules.

------------------------------------- Unconformity ---------------------------------------------

Supratrapean Laterite, lithomarge, bentonite

------------------------------------- Unconformity --------------------------------------------

Deccan Trap Basaltic lava flows with intrusive Dykes.

Out of these formations, only three types of soil are exposed within the ML area.

These are alluvial soil, Conglomeratic ferruginous sandstone and Grey Bentonitic

Clays. All other formations are revealed from quarry exposures or from the

examination of cores & cuttings from exploratory boreholes. Lignite Seams are

associated with greenish gray colored clays and carbonaceous Clays.

The lower most grey clay-bed is nearly continuous bed of varying thickness. The

grey clay / bentonitic clay are overlain by the carbonaceous clay-bed. There are

few lenses of sand, sandstone, carbonaceous clay and lignite which are

completely or partially embedded in the grey clay. The lignite lenses vary in

lateral extensions and thickness. In some locations there are more than one

lenses of lignite, grey bentonitic clay and the lenses are overlain by a

uniformly thick and continuous carbonaceous clay-bed

The lignite seam consists of brown soft and friable lignite which contains

yellow resinous material, clayey pockets and high water content.

10 11

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The lignite seam is overlain by the upper carbonaceous clay similar in

composition to the lower carbonaceous clay. The upper carbonaceous clay is in

turn overlain by the grey, plastic, bentonitic clay in which the proportion of sand

increases towards the top. The grey clay passes into the sandy clay without any

apparent break. All the rock beds overlying the lignite seam are overlain by

the uniformly thick ferruginous sandstone with a distinct angular sphericity.

11.1 Lignite of the basin:

Lignite beds in the area extend in length from Lakhanka to about 12 km and towards

north with about 1-3 km in width. The average gradient of the lignite seams vary

from 50 to 100, dipping from the edges of the basin towards the central part of the

basin. The thickness of the seam is more at the contact of trap

While it thins out towards sea.

11.2 Sub-Surface Stratigraphy:

The sub-surface stratigraphy, constituting the overburden overlying lignite seams, in

the ML area are soil, conglomeratic ferruginous sandstone & clays.

11.3 Structure:

The strike of the lignite seams is roughly North-South and dipping towards sea i.e.

eastwards. Broadly the overburden ratio increases towards sea while thickness of

lignite decreases towards Trap.

12.0 DESCRIPTION OF MINERALS

12.1 Lignite

In coal series lignite is placed between peat and bituminous coal. The

degree of qualification and type of vegetal matter are responsible for various

ranks of coal.

12

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The lignite deposit shows an abundance of plant remains in the form of

wood, stem, barks, roots and leaves. This clearly indicates that the lignite is

formed from the plant remains.

During early stages of tertiary period, the climatic conditions favored the

growth of vegetation. The torrential streams carrying such plant matter might

have formed swamps. Due to biochemical actions in the beginning the

vegetal matter might have turned into peat and subsequently in to lignite

due to dynamic thermal action. The knowledge of the lignite in this area has

been based mainly on the bore hole data.

12.1.1 Lignite

seams

The boreholes revealed the presence of two major/persistent lignite seam

with an average thickness of 4.0 meters. Two lignite horizons have been

identified and designated as top and bottom horizon respectively. A part from

these two horizons, some local seams are also formed to have developed in this

block. The variation of the Effective cumulative thickness of top and bottom

horizon is as given below.

Horizon Cumulative Thickness Minimum Maximum

Top Seam 01 2 4

Bottom Seam 02 0.33 1.5

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12.1.2 Mineable lignite seams

Lignite seams within overall stripping ratio of 1:15 (Lignite: OB) and of cut off

thickness above 0.5 m are considered as mineable seams. There are non-

mineable/uneconomic split seams with a thickness of 0.2 meter to 0.3 meter (Bore

hole No. 22) Is also observed in the center of the lease hold. Ultimate pit

bottom designed for mining cannot permit to go up to the bottom to mine

uneconomic split seams and are ignored while planning.

12.2 Overburden

The overburden formation in Lakhanka block (Khadsaliya mine lease) is

covered under a blanket of sandy soil. The overburden formations are

predominantly erinaceous in nature with small argillaceous bands represented by

clays and sandy clays.

Details about the depth of occurrence of these two horizons as given below:

Horizon Maximum

No. of

bands

Depth of occurrence in meter

Roof Floor

Min. Max. Min. Max.

Top 1 35.71 (KBH-

11

3)

74.55

(NKBH-35)

39.11

(KBH-11)

77.5 (NKBH-35)

Bottom 0 42 (KBH-

11)

79.3

(NKBH-35)

47.75

(KBH-11)

80.81 (NKBH-35)

The overburden consists of varied colored friable sandstone and clays.

Their characteristics are dealt in the Economic Minerals section separately. The

13 14

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Silica Sand is of inferior quality which can be used only after

scrubbing/processing.

12.2.1 Distribution of overburden

strata

The litho units in overburden strata have been found well distributed almost

throughout the area. While the extreme variation in thickness of the overburden

has been observed in the range of 35.71 m (KBH-11) to 74.55 (NKBH-35). The

thickness of overburden varies between 45m to 74m is very frequent.

12.3 Soil

This formation covers entire block and generally occurs between 0.00m to

1.40mThis soil is generally sandy in nature.

12.4 Sand

This litho unit is found to develop in most part of the area. It displays

various colors ranging from light, brown to dart brown, yellow and grey.

Occasionally this sand is found to be rich in argillaceous and ferruginous matter.

15

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12.5 Clay

This formation hosts lignite in most part of the area. The minimum cumulative

thickness of this formation is recorded in borehole MRP-18 as 2.30m while

maximum cumulative thickness is recorded in borehole MRP-14 as

12.6 Inter

burden

Interbred formation in the Khadsaliya lignite mine represented by clay. In most of

the cases litho units between top and bottom horizon form interbred. The

minimum and maximum thickness of interbred varies from 2.00m to 3.00m

13.0 RESERVE

13.1 Lignite

Reserves

Mining Plan was prepared taking into consideration Geological Reserves of 7.8

million tonnes based purely on CGM’s report. Considering thumb rule based

reductions, Mining & Recoverable Reserves were estimated at 6.40 & 5.76 million

Tonnes respectively, as under:

1. Gross Geological reserves ... 7.80 million tonnes

2. Net Geological Reserves (90% of 1) ... 7.02 million tonnes

3. Less in Uneconomical areas & mine slopes … 0.62 million tonnes

4. Net Reserves for mining (2‐3) ... 6.40 million tonnes

5. Less Losses in mining (10%) ... 0.64 million tonnes

6. Net Recoverable Reserves (4‐5) ... 5.76 million tonnes

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13.2 Mineable Lignite

The criteria which are taken in to consideration for mineable lignite are as

under

Cut off thickness Lignite seam 0.3 meter

Cut of depth of Lignite Seam 80.0 meter

Cut of stripping ratio 1:15

The area where Lignite seam are more than 80 m. Depth, may be up to 150

meters, a ratio of 1:15 is considered economic and cut off thickness of lignite seam

is kept 0.3m. On the basis of above criteria mineable lignite block has been

defined.

The mining losses are considered @ of 10% as such the mineable reserve of the

Khadsaliya block is 6.82 x 0.90 = 6.138 million tones.

Certain mineral remains tied up in the barriers which are to be left as per the

provision of rules and safety against nallah, river, road, adjoining lease etc. The

tied up lignite reserve for the Khadsaliya lignite block and net extractable lignite

reserve available are as under

a. Tied up lignite reserve = 0.69 million tones

b.

Net extractable lignite reserve

= 6.138 million tones

14 Exploration Data Total 66 exploratory boreholes have been drilled in the identified / Mining Lease

area, 26 nos. by the CGM prior to allocation of the Mining Lease and subsequently

another 40 nos. by the Company, in three different phases.

14. 1 CGM Report

The CGM drilled 26 boreholes in the identified area (ML area), with total drilling of

1812.43 m. Additional 21 boreholes with 1363.2 m of drilling in the area adjacent to

16

17

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the identified area (ML area), were also taken into consideration while preparing the

report by the CGM. Out of 26 boreholes falling in the ML area, lignite was

encountered in 21 boreholes.

10 boreholes were drilled at grid‐spacing of 400 m and all these jointly form the

North Block. Other 11 boreholes were drilled at grid‐spacing of 200 m (except for

325J) and these boreholes jointly form the South Block. Two prominent lignite

seams varying in thickness from 0.80 m to 8.10 m were encountered in the drilling.

The third seam of lignite, below these two lignite seams, was also countered but

only in a limited area. The maximum thickness of lignite encountered in identified

area is 9.15 m (BH no. 320). The thickness of lignite is less at the fringes while it

increases at the central part of the area. The depths of the lignite seams vary from

28.65 to 67.71 m.

Total Geological Reserves are estimated as 7.80 million tonnes, in the CGM

Exploration, with stripping ratio wise break up as under:

Below 1:5 ratio ... 877500 tonnes

Between 1:5 to 1:10 ... 2053630 tonnes

Between 1:10 to 1:15 ... 2864800 tonnes

Between 1:15 TO 1:20 ... 584350 tonnes

Between 1:20 to 1:30 ... 1123175 tonnes

Above 1:30 ... 299900 tonnes

7803355 tonnes

I.e. 7.8 million tonnes.

14.2 Borehole Density

Total No. of borehole drilled = 57

Area of Block = 171 hectare

Density of BH/Km2 = 33.33 BH/Km2

Page 24: GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) · GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) PRE -FEAS IBILTY REPORT FOR EXISTING KHADSALIYA LIGNITE MINE (Regarding Validation of

15.0 RESERVE ASSESSMENT – VARIOUS

COMBINATIONS

Geological Reserves of Lignite are assessed in the CGM report as well as in the

Mining Plan based up on data of CGM boreholes only. After drilling of NBH & KBH

series boreholes, no fresh estimate was worked out. But, recently after drilling of

NKBH series of Boreholes, the drilling agency calculated Geological & Mineable

Reserves based upon NKBH NHs only. This prompted the Company to prepare a

fresh estimate which showed much less Reserves in comparison to the Reserves

established by CGM Report and the Mining Plan. This led to the worries and this

assignment.

After study of the various reports / exploration data as discussed in the previous

Chapters, we decided to work out estimate by manual graphical (or polygon)

method as well as by taking help of some suitable software. These are discussed in

the following clauses.

15.1 Norms for Mineability:

While making assessment of Geological Reserves, all lignite seams are taken into

consideration, irrespective of thickness, quality, depth, stripping ratio, topography

etc. Assessment of Mineable Reserves needs exclusion of some BHs or their

influence zone in full or part. However, no guidelines norms were set and the

different agencies were taking into consideration their own norms. In the recent

past, the State Govt. has prescribed some basic norms for assessment of mineable

reserves.

These include:

Minimum seam thickness ... 0.30 m

Max. Depth of Seam from Surface ... 150 m

Max. Linear Stripping Ratio ... 1:15

No specific norms were provided for caloric value but by practice a CV of 2500

kcal/kg is generally taken into consideration. Based up on the discussions held with

the senior executives of the Company norms were further modified and decided for

assessing Mineability as under:

18

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Minimum seam thickness ... 0.30 m

Max. Depth of Seam from Surface ... 150 m

Max. Linear Stripping Ratio for top seam ... 1:20

Linear Stripping Ratio from seam to seam ... 1:15

Overall Linear stripping ratio ... 1:20

Calorific Value (in Kcal/kg) ... 2500

Max. Sulphur contents ... 5 %

Max Ash contents ... 20%

GHCL Ltd. - Khadsaliya Deposit

Assessment of Lignite Reserves

-----------------------------------------------------

It was also thought that while carrying out actual mining, it might not be possible to

separate out parts of seam having high Sulphur and/or Ash contents. The Company

has already installed a plant at the mine site which separates out pyrites and helps

in reduction of Sulphur content. Also in some cases, ash content is shown high but

CV falls within the acceptable norm. As such, rejection of part or full seams has not

been considered even if these constituents were found high. All other factors were

taken into consideration while deciding Mineability.

15.2 Reserve Estimation by Thickness Contour Method:

Reserve estimation is also made with help of software, drawing lignite thickness

contours, calculating area of influence of each thickness contour and then working

out the quantities. Four different exercises have been carried out for reserve

estimation Based on these different sets of BHs, as is also done in by graphical

method described earlier:

a) CGM BHs only,

b) CGM & KBH BHs,

c) NKBH, KBH & selected CGM BHs.

d) All positive Boreholes.

19

20

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However, the software developed model is just being taken as a guide line

and to understand the structure of the deposit and not for the actual

estimation purposes

16.0 GEOLOGICAL RESERVES AND GRADE

16.1 Lignite Reserves and Occurrences

The gross geological reserves of lignite of category UNFC

(111+121+221) were considered as 7.8 million tonnes

Reserve estimation plan was prepared in the scale of 1:5000 for the insitu

geological reserves in the GHCL lease and is of the order of 7.8 million tones. Out

Pit Particulars Estimate using

Mining

Software

Estimate by

Graphical

Method

1. Two Pit Model:

North Pit Ext. Lignite in mT 1.6 1.69

OB Removal mM3 35.90 32.95

Stripping Ratio 1 : 22.40 1 : 19.50

South Pit Ext. Lignite in mT 3.04 3.58

OB Removal mM3 31.77 26.77

Stripping Ratio 1 : 10.44 1 : 7.48

TOTAL Ext. Lignite in mT 4.64 5.27

OB Removal mM3 67.67 59.71

Stripping Ratio 1 : 14.58 1 : 11.33

2. Single Pit

Model:

Ext. Lignite in mT 6.06

OB Removal mM3 71.26

Stripping Ratio 1 : 11.76

Page 27: GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) · GUJARAT HEAVY CHEMICALS LIMITED, (GHCL Ltd.) PRE -FEAS IBILTY REPORT FOR EXISTING KHADSALIYA LIGNITE MINE (Regarding Validation of

of which 6.82 million tonnes will be of (UNFC 111) economical geological reserve

within the overall economic stripping ratio of 1:15 in the selected mining block.

The lignite contains Pyritious and resinous material which on oxidation

crumbles as a result it loses its compactness. Some plant fossils are

also seen. The studies conducted earlier indicate that the lignite is

mainly of attrital type constituting palaeontological assemblage comprising

of algal and fungal remains, resins, spores and angiosperm pollen etc.

Some samples are reported to be of non attrital type constituting tissues of

bark and woody elements. It is coffee brown to brownish black in color. The seam

is consistent in thickness. The thickness of overburden increases considerably

towards west.

17.0 QUALITY OF LIGNITE

17.1 Petrography of

Lignite

The lignite is of compact, compressed vegetative and ligneous matrix

showing pale brownish black color. It is friable & fine textured. Cracks and

cleavages are often seen along which the specimen splits and breaks into pieces.

Thin films of clayey matter are also present along the fractured planes.

Microscopic examination reveals two types of constituents namely semi

xyloid and amorphous type among the samples. The xyloid component retains

some structures. The nature and arrangement of the pores and rays suggests

dichotomous plant forms of angiosperms. The material seems to be composed of

twigs and branches, since the lignite is of recent age (Eocene) fungal remains

are preserved together with plant tissues.

17.2 Chemical

Composition

21

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The results of proximate analysis of lignite indicate high ash content, varying from

13.60% to 63.92% and high Sulphur content. The high ash content is due to high

mineral matter in it. The high Sulphur is due to inorganic constituents such as

marcasite and pyrite developed under sub-aquatic depositional conditions. The bed

moisture content of lignite usually varies from 35 to 45% while on air dried basis, it

varies from 4.1 to 24.94%. A statement showing thicknesses of different seams

encountered in boreholes along with quality parameters is attached as

.i) Proximate Analysis: The proximate analysis of lignite samples showed following

variations Table Results of Proximate Analysis of Lignite Samples

Particulars Minimum (%) Maximum (%) Weighted (%)

Average

Moisture 4.10 24.94 10.21

Ash 13.60 63.92 30.37

Volatile Matter 17.55 43.92 33.89

Fixed Carbon 11.38 34.88 24.61

Calorific Value (Kcal/Kg) 1849 5134 3603

18.0 TRANSPORT SYSTEM

Lignite is being transported from the mine pit to the lignite stock . The lignite

mined by hydraulic excavators is loaded on to the trucks. After the loading, the

lignite is weighed at the weighbridge and then moved to the destination Sutrapada

plant (Lignite is for only captive use).

18.1 Transportation of Men and Material

The Staff buses are carrying the men during shift hours Senior Managers are

provided with Car for constant monitoring of the mine working.

22

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19.0 WATER PUMPING AND DRAINAGE SYSTEM

19.1 Surface

Water

The surface water flowing in Satrunjay cannel will not be affected at any

time as sufficient precautionary measures have already been taken.

19.2 Ground

Water

As the ground water below lignite horizon will not be exposed at any time

during mining operation, the quality of the ground water will not be polluted.

20.0 METHOD OF WORKING

20.1 Method of

Mining

The Khadsaliya lignite mine is proposed to be operate by mechanized opencast

method of mining with conventional mining equipment i.e. Shovel and

dumper combination. The overburden strata is soft and clayey which does not

require any blasting and can be easily excavated by hydraulic excavators,

including lignite seam.

The overburden is proposed to be excavated by hydraulic excavator of 0.9

to 2.5 M3 bucket capacity with matching size of haulers (dumper) of 16 T and 35

T. capacity The excavated overburden shall be stacked on proposed waste

dump site and it is also proposed to use OB for back filling of the decoaled

area of existing Khadsaliya block which is on north side of the this block at an

average lead of 1 to 1.5 km. The overburden shall be dumped and pushed down

and leveled by dozers. The average gradient of haul road shall be 1 in 16 except

short ramp of 1 in 10, which shall be made as and when required of small stretch.

The haul roads and ramp proposed shall be regularly graded by

graders and maintained in good condition.

23

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20.2 Bench Geometry

Since the overburden strata is soft and of low comprehensive

strength, bench geometry of 5m height and 5m widths is proposed for

stability. It is also proposed to keep every 3rd of 7.5 m wide, which will reduce the

overall slope of the benches to ensure better stability.

Height of bench - 5 m Width of

bench - 5 m

The overall slope - 360 (1 in 1.5)

The bench width of development and advancing faces shall be kept 20 m to 30 m

wide to facilitate safer movement of the machineries.

20.3 Quantum of Lignite production and OB generation

24 25

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20.4 supporting composite plan showing pit layout dumps, stack

of top soil is enclosed please refer plate no. 4/I. (Present mine plan)

Sr. Financial Production from Mines Over burden Removal Over burden

Removal OB

No. Year SOUTH PIT NORTH PIT TOTAL SOUTH PIT NORTH PIT TOTAL Ratio

(Qty in Mt). (Qty in Mt). (Qty in Mt).

(Qty in

Cum)

(Qty in

Cum) (Qty in Cum)

on Total

OB

1 2004-05 73884.861 0 73884.861 3029700.96 0 3029700.962 41.005707

2 2005-06 165906.101 0 165906.101 2094882.43 0 2094882.434 12.626916

3 2006-07 158202.447 0 158202.447 4032839.01 0 4032839.013 25.491635

4 2007-08 91359.347 0 91359.347 745581.332 0 745581.332 8.1609748

5 2008-09 232977.968 0 232977.968 1943395.76 0 1943395.761 8.3415431

6 2009-10 311575.455 0 311575.455 2925958 0 2925958 9.3908488

7 2010-11 306103.525 0 306103.525 2690284.32 0 2690284.324 8.7888054

8 2011-12 394033.843 0 394033.843 3397267.27 0 3397267.273 8.6217652

9 2012-13 313032.574 0 313032.574 4772200.37 0 4772200.368 15.24506

10 2013-14 190096.185 0 190096.185 2914410.34 1086138.68 4000549.021 21.044867

11 2014-15 142140.219 57768.1725 199908.391 84895.456 4666861.18 4751756.633 23.769671

12 2015-16 0 91860 91860 0 2885574.97 2885574.967 31.412747

13 2016-17 0 78460.483 78460.483 0 1106297.11 1106297.109 14.100055

14 2017-18 0 56532.7965 56532.7965 0 1058228.94 1058228.938 18.71885

15

2018-19

(Till

Nov`2018) 0 63946.031 63946.031 0 1333914.92 1333914.916 20.860011

Total 2004-05

to 2018-19 (Till

Nov`2018) 2379312.52 348567.483 2727880.01 28631415.3 12137015.8 40768431.05 14.945097

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20.5 Rate of lignite production and life of the mine

First five year

capacity-

Initially the capacity of mine proposal low as the overall stripping

ratio is 1:15 and according the development is to be carried out.

The mine will reach to its rated capacity of 0.40 mill tones in 5th year

starting from 0.073 lakh tones in first year. The overburden removal target

is slowly increased as it’s requires lot off capital investment and after

generating sufficient revenue in succeeding years the management

shall be capable to operate the mine at its rated capacity.

a.

b.

Annual target of lignite production

Total mine able reserve

=

=

4, 00,000T

6.82 M.tonnes

c.

d.

Production in first five year of

Mining Balance at the end of 15th

year

=

=

0.719 M tones

3.03 M Tonnes

e.

Life of the mine at the end of 15th

year

= .

08 yr

f. The total life of the mine = 15+8 = 23 year.

26

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20.6 supporting composite plan showing pit layout dumps, stack of top soil is enclosed please refer plate no. 4/I.

27

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Life of Mine

The life of the Khadsaliya lignite mine deposit is 23 year as per the mining

scheme and annual Capacity of 4, 00,00T of lignite production proposed. In

case, if annual production capacity could not achieve, life shall be increased in

that manner.

Market Demand and Life of the mine

The above lift of the mine is estimated on the rated capacity of 0 .40 mill tones of

lignite production. But the lignite production is directly linked with the market

demand and as such there will be up and down in the proposed lignite

production annually, in such cases there is possibility of extension of life of the

then estimated one

The Khadsaliya lignite deposit is proposed to work by mechanized opencast

mining method with conventional mining equipment’s i.e. shovel and dumper

combination. The Strata is soft including lignite hence can easily be

excavated by hydraulic excavator without blasting. Higher capacity excavator

of above 3.5 m3 bucket capacity proposes the overburden removal with 35 T

matching size dumpers. The lignite production is proposed by 1 m3 bucket

capacity excavator considering nature of lignite.

The deposit shall be opened up by driving a ramp of 20 m width of 1/16 gradient

from South-East side and will approach top of lignite seam at a depth of 43 m

from surface at borehole no. KBH-9.

The ramp shall be driven from North-East to south-West in the ultimate

mine pit benches of East side. The mine working (active) faces are proposed to

advance from East to West direction, x-section of mine workings. The

overburden generated in first two year is proposed to stack at proposed

site on North-west side. Where the height of dump is proposed 30m to

keep land degradation minimum. The

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O.B. generated in 3rd year is proposed to back filled in decoaled area of

adjoining

Existing operating block. Another waste dump site is also proposed on North-

West side to accommodate future OB generated. The back filling shall be

carried out from the 4th year beginning at decoaled area on southern

boundary of the deposit. Separate stack is also proposed for stacking of

top-soil available during excavation.

21.0 INFRASTRUCTURAL FACILITY

21.1 Site Services

The infrastructure facilities to this mine are explained here and will

include the provision of the following:

• Mine site office

• Mines Canteen cum rest shelter

• Mines vocational training center

• First aid room

• Electrical sub station

• Weigh bridge with cabin

• Approach road from village to mine

• Security office cabin

• Pyrite nodule separation plant

21.2 Construction of Weigh Bridge at Mines

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One Mechanical Weighbridge is exclusively kept for weighment of lignite,

installed near administrative building and main road for easy transportation of

lignite after weighment.

21.3 Supply of Electric Power

One 11 KV overhead line from which the electricity is stepped down to

440 V substation near mines canteen. This power is sufficient for mine

lightings and for the pump age of water. In addition to this, 125 KVA DG sets are

available to provide emergency power requirement for pumping.

21.4 Supply of Drinking Water and other Water Required for Dust

Suppression etc.

The drinking water for person employed in mines, domestic use and water

required for dust suppression.

21.5 Transportation of Men and Material

The Staff buses are carrying the men during shift hours. Senior Managers are

provided with jeep for constant monitoring of the mine working.

21.6 Communication System

P&T telephone network is available at office premises. Mines managers are also

provided mobile for instant communication purpose.

21.7 Medical Facilities

1 nos. of ambulance van for emergency transport of injured or patient.

Periodical medical examination of all the staff is regularly being done with the

help of dispensary.

21.8 Employment Potential

29 30

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The man power required for the production of 1.0 million tonnes per year is as

follows:

S. No. Designation Qualification Strength

1 Agent/Mines Manager First class (coal) 1

2 Safety Officer “ 1

3 V.T. Officer “ 1

4 Asstt. Manager (Mines) Second class 3 *

5 Colliery Engineer Mechanical degree 1

6 Over Man /Foreman certificate holder 1

7 Mining Sirdar/mate “ 1

8 Mine Surveyor “ 1

9 Labor welfare office 1

10 H.E.M.M. operators

(Excavator, Dozer, Dumper,

54

11 Spotter 1

12 Mechanic 1

13 Auto Electrician 1

14 Electrical Supervisor 1

15 Pump attendant 1

16 Time keeper 1

TOTAL 72

* One Asst. Manager shall have first class (Coal) certificate.

22.0 CAPITAL COST ESTIMATE

Total capital cost is appx. 2400 Lakhs towards mining equipment to

produce lignite.

23.0 ENVIRONMENTAL MANAGEMENT PLAN

Environmental protection and control is now a global concern. The deterioration

often results from the activities by human being by extraction of minerals. It is

imperative that in order to ensure continued and sustained progress of

the mining industry, the environmental dimensions should be

31

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integrated in to the planning, design, development, and operation and

working practices of mining on scientific and rational lines.

Every new mining project is appraised by detailed EIA/EMP, which is a

statutory requirement under Environment Protection Act, 1986. Open cast

mining involves excavation and movement of large volumes of Earth crust.

These operations have multi facet effect on environment and the eco-system.

Therefore, the environment management system is very important in open cast

mining and it can be implemented by proper monitoring and control systems.

Environmental Protection Cost

SN Activity Lump Sum cost (Rs. In Lac)

PMC

Period

FMC

Period

Post

Closure

Total

Provision

1. Barbed wire fencing around ponds,

Temple & Oxy. Park, Children park

& Playground etc. with suitable gates etc.

20

20

10

50

2. Dismantling of Plant & other

structures and cleaning of site inclusive of

transportation of material away from site

-

10

20

30

3. Development of Children Park

with fruit bearing trees, Library & Play Ground

35

-

-

35

4. Plantation for Oxygen Park

-

30

55

85 Development of Hill top Temple

With water supply & storage arrangements.

5. Development of Green Belt 10 - - 10

6. Development of Ponds along with

provision of stone-pitching, retaining walls,

water over-flow point etc.

25

35

40

100

7. Land Reclamation (Re-handling &

Spreading of top soil over backfilled area and

Development of Gauchar Land by planting trees,

shrubs & fodder.)

300

300

150

750

8. Provision of surface drainage

system

10

10

5

25

9. Repair and development of Internal

Roads

-

15

5

20

10. Supervision & Post Closure -

Environmental Monitoring

-

-

50

50

11. Provision for Trust Fund - - 50 50

TOTAL 400 420 385 1205

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Amount Of CSR Activity Contributed In Last 05 years – By Khadsaliy Lignite

mine GHCL. DETAILS OF PROPOSED CSR ACTIVITY:

33

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AMOUNT OF CSR ACTIVITY CONTRIBUTED IN LAST 05 YEARS – By GMDC

LTD.

Year

2013-2014 2014-2015 2015-2016 2016-2017 2017-2018

Amount in Rs. 1985481.55 2411650.42 1002259.04 1398767.2 603648.76

24.0 BASELINE INFORMATION

24.1 Existing Land Use Pattern

The corporation possesses the surface right for the current mining lease

for the private survey numbers lying in the Khadsaliya lignite mine lease

and rest of land is government waste land.

24.2 Water Regime

The Satrunjay cannel which flows on the East side of the deposit and is a

seasonal one, which carries water only in summer months. For a few day.

There are tube wells in the nearby villages and are used by the

villages for drinking eastern side of village Khadsaliya. In Khadsaliya

village the water table in tube well is at about 50.

2019 2020 2021 2022 2023

More than 2.0 % of profit will be contributed to

need based CSR activity on first come first

requirement.

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24.3 Climatic Condition

The monsoon here is generally heavy compare to other part

of Gujarat, which generally start in late June and continue up to middle

of September. Average annual rainfall is 550 mm. Winter month to

pleasant. The temperature during post monsoon goes down to 12.5oC and

summer months goes above 430C.

24.4 Flora and Fauna

The floral species found in the whole of the study area representative of

the “6/E3-Rann saline Thom scrub forest type” under the forest type

classification of champion and seth. private land owners grow cotton

Bajra, Jowar, Tuvardal and pulses etc. For their lively hood. Neem

trees, mango trees, Banyan trees, etc.

24.5 Human Settlements

There is no human settlements is required for the Khadsaliya Lignite block.

24.6 Quality of Air & Water

The quality of water is within the prescribed limit as per available data.

The quality of ambient air is within the permissible limits of 3mg/cubic

meter inside the mine. Dust suppression is regularly being done through water

spraying.

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24.7 Whether the Area Falls Under Notified Area under Water Act, 1974

This area does not form part of area notified under water Act, 1974.

24.8 Cropping Pattern

Out of 171.0 hectare of lease hold area only 42.26 hectare of lease hold area are

private lands where crops like cotton, Bajra, Millet and pulses are being

cultivated by the villagers.

24.9 Existing of National Park, Wild Life Sanctuary, and Reserve Forest

Etc.

No national park and wild life Sanctuary etc. Is located in the vicinity of the

lease hold area. 42.224.10 Preparation of EIA & EMP

The collection of base line data for the preparation of comprehensive EIA & EMP

will be carried out after getting TOR. One season data along with the possible

impact on air, water and the present eco system due to mechanized

mining and solid waste disposal will be carried out separately..

The ambient air quality survey, water quality survey including ground water, soil

quality survey, noise level survey has been carried out systematically as

per the guidelines issued by the Ministry of Environment and Forests, New

Delhi.

25.0 ENVIRONMENTAL IMPACT ASSESSMENT (EIA)

Mining activities generally entail change and disturbance to the

environmental and ecological set-up in any area with respect to various

components like Land, Air, Water and Soil quality, Noise levels, socio-

economic patterns, Flora-fauna status etc. Such changes and disturbances

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constitute the impact of the mining operations on the various environmental

component, which could be either nullifies or attenuated by adoption of

proper control measures to correct the adverse impacts. By understanding the

impact in the context of mining in Khadsaliya lignite mine on environment can be

broadly categorized and measured as under.

26.0 ENVIRONMENTAL MONITORING

For the Environment Impact Assessment and to further prepare the EMP,

CSIR- CIMFR Dhanbad, has been identified as an agency. They will carrying

out the Impact Assessment studies after getting TOR by the MOEF, New Delhi.

26.1 Air Environment

In order to have correct environment & to further prepare the EMP, CSIR-

CIMFR Dhanbad, a modal agency in the field of study of environmental

parameters has been identified to undertake the job.

26.2 Water Environment

The water regime in surrounding areas and mine is also with in the

norms of CPCB. The water regime in other areas is reasonably within

limits as per available old EIA- EMP .

26.3 Noise Environment

The Noise levels in and around existing mine within the stipulated zone

were found within prescribed limits specified by Director General of Mine

Safety. As per available old EIA-EMP.

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26.4 Land Environment / Land Use Planning

The important parameters of land use planning are soil characteristics,

present land use, climate, topography and socio-economic status and future

requirement. Land use in mining areas consists of mainly forestry and agriculture.

Mining activities introduce change in the land utilization pattern. The grazing and

agricultural activities by the locals are hindered/reduced. Proper land use

planning becomes a basic requirement for a mining project. To prevent air, water

and soil pollution is also utmost important in restoring the eco-system in total.

These efforts coupled with rehabilitation, restoration and reclamation of the

mined area helps restoring the environment.

For the purpose of evolving land use in mining areas basic knowledge of plant

growth is necessary. The Central Board for prevention and control of water

pollution (1980) Suggested that the land use planning in mining areas

should be prepared to encompass pre-operational, operational and post

operational phases/scenarios. Generally the environmental balance of the

area is adversely affected due to large open cast mining operation. The

environmental imbalance caused by mining operations can be offset and

the land can be reclaimed to restore the original shape of landscape for

afforestation, grass fields and any other habitation. The reclamation process

starts in the 3rd year of mining operations in the Khadsaliya Lignite lease.

The cavity created will be backfilled and leveled so that a smooth-surface profile

is maintained.

While excavating, the top soil is dumped separately. When the refilling operations

begin, the top soil is brought back on to the surface to increase the fertility of the

soil on which plantation is proposed. Due to this, the original vegetation of the

area can be grown again without any extra effort.

During the initial mining operations of two years, the rejection is disposed to the

waste dump yard situated east of proposed initial mine cut. Once the cavity is

filled up and graded the plantations will start after restoring the top

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soil with proper manure (Phosphate fertilizers & nitrogenous fertilizers)

added to the soil. Generally the mined out soil is alkaline and moisture

absorption capacity is poor. Gypsum treatment may also help for better growth

of plants. The water accumulated in the pits during rainy season can also be

used for maintaining the plants at least for a period of two years.

Local species like Baval, Neem, Sisam, Sitafal will be selected for

afforestation.

Land Use Pattern for the Khadsaliya Lignite Mine

Land Use Pattern:

a) Pre Mining Operations (Original):

- Private Agri. Land : 42.26.71 Ha

- Gauchar (Pasture) : 128.73.29 Ha

- TOTAL : 171.00.00 Ha

b) Progressive Closure Land-use (After 2 yrs. from now):

a) Total area broken for mining : 110 Ha

Area Reclaimed by backfilling up to OGL : 52 Ha

Area Developed & restored to effective use as:

i) Temporary Small Pond : 2.54 Ha

ii) Children Park, Library &Playground : 2.00 Ha

b) Area under External OB Dumps : 32.92 Ha

c) Area under green belt : 4.95 Ha

d) Pyrite Separation Plant : 2.50 Ha

e) Other Infra-structures & Road : 3.00 Ha

f) Nallah & other undisturbed area : 17.63 Ha

TOTAL (a + b to f) : 171.00 H

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c) Proposed Post Mining Land Use (On Final Mine Closure):

- Gauchar : 129.00 Ha

- Water Reservoirs (2 Nos.) : 39.00 Ha

- Children Park & Playground : 2.00 Ha

- Dump-top Temple & Oxygen Park: 1.00 Ha

TOTAL : 171.00 Ha

27.0 MEASURE FOR DUST SUPPRESSIO

In order to ensure that the air does not get polluted with the dust

generated during mining, necessary protective measures are important to

keep the atmosphere free from pollutants.

a. Spreading weathered trap rock and compaction of the mine roadways at

every six months and watering them daily in all three shifts.

Dust hazard is at the maximum during dry season due to movement of vehicles.

Due to strong winds fine materials become airborne and it may

affect neighboring villages.

b. The dumpers/trucks should not be over loaded so that the spillage of

materials can be reduced through which dust is generated.

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c. Providing rows of trees of different heights on both sides of the road, will

arrest the dust by acting as a barrier.

d. Periodic measurement of dust fall should be taken for monitoring. It is

advised that at any spot in the mine, the dust level should not exceed 3 mg/m3.

The dust level in the normal residential areas should be maintained below 0.2

mg/m3.

e. All dust below 5 microns is usually considered dangerous. They are

reparable dust, which can harm the lungs. At one percent solution of calcium

chloride in water acts as an excellent dust suppresser. Sprinkling of the

water mixed with CaCl2 greatly reduces the hazard in opencast mines.

27.1 Measures to Minimize Vibration Due to Blasting and Check Noise

Pollution

Since the overburden removed for the production of lignite is soft no

drilling and blasting is required in the mine. Hence no protective measured

are proposed to contain the noise pollution.

28.0 AFFORESTATION PROGRAMME

28.1 Stabilization and Vegetation of Dumps

Dumping of mine waste cause the maximum damage to the environment.

Reclamation can be done to minimize the pollution. It involves the application of

basic principles of soil and water conservation, afforestation, regeneration of

vegetation and pollution control.

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The dumping areas can be identified as under

a. Proposed dumping area

b. old/inactive

dumps

c. Inside dump /Backfilled dumps.

The places at which afforestation planned is marked in the stage plan at the end

of fifth year.

28.1.1 Proposed dumping area

The outside dumping yards have been proposed on West side at Northern end

. The proposed height of the dump is 30 meter in three lifts of 10 meter each

there by restricting the height to 30 meters as the area is prone to high wind

velocity, which may be carried in the wind. A road with 10 meters width is

suggested between the first and second stage dumping so as to minimize

any collapsing and also to keep optimum angle of repose for the dump soil.

The over burden benches will be leveled regularly by dozer which will compact

and settle the materials to protect slides.

28.1.2 Old dumps

As soon as a dump becomes inactive, the environment protection work starts on

waste dumps which are called old dumps. Selected grass species Babool are

planted in area of old dump. Grasses have grown successfully. Grasses are not

only preventing soil erosion but also spreading bio-activism in the dumps,

which is necessary for plantation. More than 1,00,00 saplings were

planted on these dumps parapet wall will also be constructed surrounding

the inactive dumps so as to avoid soil erosion. Terraces will be formed at

two meter interval along the slope of dumps and selected tree species will

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be planted. This type of plantation system will bind the dump materials to

protect any further collapse of materials and also for better plant growth.

28.1.3 Inside Dump

yard

After three years of completion of outside dumping infilling dumping will

be started in the excavated area. Fourth year of operation onwards the

over burden shall be dumped inside the pit which will have three sides

bounded by the mine pit benches.

Therefore it is more stable compared to outside dump yard. At the end of 10th

year the abandoned pit can be used as a storage pond which will be

used for irrigation or watering plants in dumps and other leasehold area which

is barren may be allotted to the forest department for planning and executing

afforestation programed. Since they have a routine afforestation programed,

they may agree and do afforestation in the mined out areas.

29.0 MEASURES FOR MINIMIZING ADVERSE EFFECT

ON WATER REGIME

29.1 Treatment and Disposal of Water from the Mine

The water accumulated in the mine pit due to seepage and due to rain is

proposed to utilize for plantation after treatment. Quality is regularly checked and

pH is measured daily.

29.2 Measures for Minimizing Adverse Effect on Water Regime

29.2.1 Ground Water

As the ground water below lignite horizon will not be exposed at any

time during mining operation, the quality of the ground water will not be polluted.

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29.3 Socio-Economic Environment

Khadsaliya lignite mine GHCL is in operation since 2004. The core zone of

this mine is covering the lands of Khadsaliya village. Mostly Koli population

is living in this village. Their main occupation is farming, mine workers,

agricultural workers, contractor workers, drivers and helper’s etc. Local people

have been provided appointment in the mine as labor work. Panipurbatha

department is providing drinking water in the villages Khadsaliya regularly.

Children are given study material facilities. Regular help is extended in

education and medical facilities by the Corporation. Corporation has also

constructed water tanks.

An adequate awareness is shown to prevent pollution at the stage of project

execution. It will be taken as moral obligation rather than a statutory requirement.

29.4 Ecologically Fragile Area

The work group constituted by the Department of Environment has

recommended some areas/ eco-system, which has been identified by the task

force as Ecologically fragile area where no mining activity can be

carried out.The fragile areas are supposed to have richness, susceptible to

species loss, with aquifers and susceptible to seismic hazards.

There is no area with the above criteria located in the lease hold or in

the vicinity. Therefore no area is identified as Ecologically Fragile Area.

29.5 Conceptual Mining Plan

The ultimate mine pit limit boundaries at the end of 5th year and at the

end of 10th year. The stage plans depict the area to be reclaimed for the

purpose of plantation. Dumps are also considered for plantation once they

become in active.

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29.6 Disaster Management Plan

The following are the major disaster which can be expected in a lignite

mine.

a. Flooding of mines

There is no possibility of Cannel water entering in to the mine. As per practice,

mining operations gets suspended during the monsoon period. All machinery

and manpower is withdrawn at a safe place. Water level is

continuously observed in each shift by the competent supervisors and officers in

order to take necessary and safe precautions. Only pumping operation is being

done at a safe identified place.

b. Fire disaster in the mining area, machineries, workshops, stores, oil tank etc.

since the mined out lignite will stacking there is no possibility of fire

catching on lignite. The exposed lignite faces will be covered with an

overburden of 0.5 meters. Stripping of this half a meter O.B. will be done just

before the loading takes place. As far as the carbonaceous shale is

concerned they will be stacked separately in an old dump.

As far as the fire at mining sites is concerned sufficient fire extinguishers and

firefighting equipment’s will be provided with necessary accessories etc. by the

GHCL. This will be maintained in various premises for emergency

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