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GEOLOGICAL AND ENVIRONMENTAL STATUS OF MAKRANA MARBLE MINING AREA NAGAUR DISTRICT, RAJASTHAN AND STRATEGY FOR SUSTAINABLE DEVELOPMENT

by admin last modified 2007-11-13 16:52

J. V.   NATANI

Geologist  (Sr.), Geological Survey of India, Western Region, Jaipur

 

INTRODUCTION

 

Makrana (27º02’25” N latitude, 74º43’44”E longitude) is situated at eastern margin of the Thar desert and has an ancient marble mining history.  The Makrana marble has made a perceptible dent in marble industry because of its blockability, whiteness, high CaO 50-56 %, low MgO 0.90–177 %, as compared to other marbles of Rajasthan (Table - 3), good polishing character and lustre. It is fine grained and exhibits stable, well distributed colours, pleasing and attractive designs and patterns. The translucent varieties of Makrana marble are preferred over other marbles for monumental and sculpture work (IBM 1993).

 

GEOMORPHOLOGICAL AND GEOLOGICAL SET-UP

 

Geomorphologically, the area is represented by strike ridges, sand  sheets, anthropogenic overburden mounds, slurry dumps and deep pits.  Drainage in the mining area is mostly internal. Major part of the area is covered by mobile to semi stable, NNW-SSE to NE-SW trending sand dunes which overlie calcareous sand pseudo-conglomerate, kankar or gypsite bed of Quaternary period.  Marble is exposed on surface in the central part, whereas overburden varies upto 15 m in the northern and the southern part of the area.

 

General slope in the mining area is towards west and northwest.  Ground water in the area occur under water table condition and mining at present is below water table in old mines.  Water table is 30-40 m below ground level.  Ground water from the mines is released in open lands and agricultural fields. 

         

Makrana marble deposits belong to Ajmer Formation of Kumbhalgarh Group of the Delhi Supergroup (Pareek, 1984; G.S.I. 1997).  Five prominent marble bands occur in the area west of Makrana.  From east to west these are known as (1) Devi-Gunawati range (2) Dungri range (3) Pink range, (4) Makrana Kumhari range, and (5) Borawar Kumhari range with band I and II (Natani, 2001).  The different marble bands have formed due to tight isoclinal folding. The mining ranges are known by different names in different blocks (Fig. 1).  At present mines extend from Matabhar in the north to Bilu-Mored in the south (approximately 13 km) along the strike and from Gunawati in the east to Borawar in the west (about 1.6 km) across the strike.  Matabhar, Kalanada, Kolhadungri and Bilu-Mored are new mining areas.  Details of various marble bands/mining ranges exposed around Makrana are given in Table - 4.

map copy.jpg

 

MINING RELATED ACTIVITIES AND THEIR IMPACT ON ENVIRONMENT

 

Open cast mining, marble processing, solid waste generation and its disposal, trading and transport of marble blocks, slabs and irregular marble pieces (khandas), and art and craft work are important activities in Makrana mining area.  Quarrying is by conventional rope and bucket method and the quarries run along the strike and dip of marble bands.  Large scale land transformations, unscientific mining, unsegregated waste dmps, incompatible land uses and improper waste disposal have caused land degradation, ponding and flooding of water, visual impact, loss of aesthetics, pollution, health and safety hazards.

 

ENVIRONMENTAL IMPACT ASSESSMENT METHODOLOGY

 

The impact assessment was done by means of a semi quantitative graded matrix (Leopold, Clark et. al. 1979) to assess the over all impact of mining and related activities on environment. Matrix method basically incorporates a list of project activities or actions, which affect the environment (listed in columns in matrix table) and environmental parameters (listed in rows) as shown in the Table-1. Environmental parameters were weighted so that they could be correlated to each other in terms of relative importance. Positive and negative signs were assigned to the impact value of each parameter to show beneficial and adverse impacts respectively. The impact values were assigned as per scheme shown below :

 

Impact Value

Impact nature

Remarks

0

No impact

 

1

Slight impact

 

2

Appreciable impact

+ sign denotes beneficial impact

3

Significant impact

- sign denotes adverse impact

4

Major impact

 

5

Severe / Permanent impact

 

 

Impact value of each parametre was multiplied by the weightage values allotted to the corresponding parametre. This gave final score in terms of environmental impact units. Summing up the final score gave environmental impact assessment of the entire project / mining area. Significance of total environmental impact score is given in table 2.

 

The environmental impact assessment followed identification and quantification of impacts. The project activities which have impacts on various environmental parametres in Makrana are enumerated below and quantified in Table-1 and 2.

 

1

Mining

Includes pitting, blasting and excavations.

2.

Processing

Includes Edge cutting, buffing, polishing tile making and processing waste from crushing and chip making plants.

3.

Waste disposal

Includes disposal of overburden strata comprising soil, silt, aeolian sand, calcareous sand, mine muck and mining waste comprising of pegmatite (Shaly)*, calc silicate rock (Bhanwara)*, dolomite (Jhond)* and quartzite

4.

Slurry disposal

Includes disposal of marble slurry.

5.

Transportation

Mainly by trucks, water tankers, slurry tanks mining machinery, donkey carts etc.

6.

Arts and Crafts

Includes activities of sculpture making, monumental work, flower vases, kitchen ware, idols, table tops and other handicraft items.

7.

Trading

Daily traffic of buyers, brokers etc. and interaction of seller, buyers and brokers.

* - Local names prevalent in mining community for waste rocks.

 

Table : 1 -  Importance value of Environmental Parameters-Makrana

 

Environmental Parameters

 

Ranking

Total

Weightage

Parameter Importance Value

 

1

2

3

4

5

 

 

(PIV)

1.Soil and Land

 use

 

 

 

 

 

*

5

5/30

        165

2. Water resources

 

 

*

 

 

3

3/30

100

3. Air and Noise

 

 

 

*

 

4

4/30

130

4. Flora and Fauna

 

*

 

 

 

2

2/30

  70

5. Socio economics

 

 

 

 

*

5

5/30

165

6. Civic amenities

 

 

*

 

 

3

3/30

100

7.Health and

 Safety

 

 

 

*

 

4

4/30

135

8. Aesthetics

 

 

*

 

 

3

3/30

100

9.Human Settlements

and historic

 buildings

*

 

 

 

 

1

1/30

  35

 

 

 

 

 

 

 

S

 

30

 

 

Ranking on impact scale

0          -    No impact, 1 -Slight impact, 2  - Appreciable impact,3 -Significant impact, 4       -           Major impact, 5 -Severe / Permanent impact.

 

Table-2 :  Environmental impact Matrix of Makrana mining area  (without mitigative measures)

 

 

PROJECT ACTIVITIES

Total

PIV

Environmental

Parametres

 

Mining

 

Processing

Waste disposal

(overburden & mine muck)

Slurry disposal

 

 

Transportation

Arts &     crafts

 

Trading

impact score

 

 

1

2

3

4

5

6

7

(TIS)

165

Soil and Land use

-4

-3

-4

-4

-1

o

-1

-2805

100

Water resources

-3

-2

-2

-2

o

o

-

-900

130

Air and Noise

-3

-3

-3

-3

-2

-1

-1

-2080

70

Flora and Fauna

-1

-1

-1

+1

-1

+1

-1

-210

165

Socio economics

+5

+5

+2

+3

+5

+5

+5

+4950

100

Civic amenities

o

O

-1

-1

-1

+2

+2

+100

135

Health and Safety

-3

-1

-2

-2

-2

o

-1

-1485

100

Aesthetics

-4

-2

-3

-3

-2

+5

-2

-1200

35

Human Settlements

and historic buildings

-3

+2

-1

-1

-1

o

o

-245

 

 

 

 

 

 

 

 

TIS =

-(3875)

 

ASSESSMENT VALUE INDEX

TIS

 

Impact Assessment

upto  (-) 1000

-

No appreciable impact on environment

(-) 1000 to (-) 2000

-

Appreciable impact on environment; but not injurious in general. Mitigation measures important.

(-) 2000 to (-) 3000

-

Significant impact on environment. Major environmental control measures to be taken.

(-) 3000 to (-) 4000

-

Major injurious impact on environment, Major environmental control measures to be taken and / or site selection for the proposed project to be reconsidered within the buffer zone.

(-) 4000  and above

-

Alternative site for the proposed project to be selected out side the buffer zone.

 

Table – III Chemical Composition of important marble deposits of Rajasthan and world

 

Chemical

composition

       World  famous

  Carra, *

   Italy

Marbles

 Pentelinkar*

  Greece

                        

Makrana, **

India

Theoritical

Calcite***

Theoritical

Dolomite***

 

Makrana

 

Rajnagar

Rajasthan

Aandhi

Marbles+

 Banswara

 

Sirohi

 

Udaipur

 

CaO

 

NA

 

NA

 

56.08

 

  56.00

 

NA

 

50-56

 

30-33

 

26-34

 

32

 

51.49

 

20.79

CaCO3

99.35

99.85

100

100.00

30.4

NA

NA

 

 

 

NA

MgO

N.A.

N.A.

0.90

Nil

21.29

0.79-1.77

16-25

18-21

23-24

  0.90

2.21

Mg Co3

0.87

0.33

Nil

Nil

N.A.

N.A.

N.A.

 

 

N.A.

 

SiO2

Nil

Nil

Nil

Nil

N.A.

0.00-1.20

0.01-7.6

.01-3.2

Up to 23.4

8.52

14.35

Fe2O3

Traces

0.05

0.22

Nil

N.A.

0.10-0.28

0.12-0.95

0.73-3.2

0.20-0.84

0.54

0.28

Al2O3

0.11

Nil

0.04

Nil

N. A.

N

N.A.

N.A.

N.A.

N.A.

N.A.

Insolubles

Traces

Traces

0.46

Nil

N.A.

N.A.

N.A.

N.A.

N.A.

N.A.

N.A.

LOI

N.A.

Nil

43.28

44.00

47.7

34.82-44

36-44

40-47

42-44

39.36

24.00

Data source 

*   IBM  Market Survey Series  MS : 1993,

**      Heron  1953  p 165

 ***   Petti John 1949, p. 314, 

+        Natani 2001

N.A – Not Analysed/Not available

 

Table – 4 Details of Various Marble Bands / Mining Ranges Exposed Around Makrana, Nagaur District; Rajasthan

 

 

Mining ranges / ridges from west to east

Western most ¬

Borawar Kumhari

 

 

 

®Eastern most

 

 

 

 

Borawar

   Kumhari

Makrana-Matabhar

        Kumhari

 Makrana Pink

Dungri

 

Devi - Gunavati

S. No.

CHARCTERISTICS

BK-II

BK-I

MK

MP

Cd

 

N

Kala Nada

 

Ulodi

­    

Chausira

 

Gunavati

 

Pahad kuva

¯

Bhont

 

Kolha Dungri

S

Bilu - Mored

1

2

3

4

5

6

7

8

2.

Strike Length / Extension.

0.5 km

0.2 km

4.3 km

4.0 km

4.5 km.

12.0 km.

3.

Strike and Dip.

NNE-SSW to N-S

55°-80°®E

NE-SW to

NNE-SSW

55°-80°®E

NNE-SSW

60°-75° ® E

NNE-SSW

50°-80°®E

NNE-SSW

60°-70° ® E

NNE - SSW to NE - SW

60° - 80° ® E

4.

Width

30 – 40 m

30 - 40  m

40 - 50 m

35 - 70 m

60 - 80 m

90 - 150 m

5.

Colour

Greyish black

Greyish black

Greyish with black lines

Pink

Bluish white, White with brown base, White with Grey, Brown and bluish bands.

White with dark bands in Albeta type

6.

Granularity

Medium to Coarse

Medium to Coarse

Medium

Fine to medium

Fine to medium

Fine to medium

7.

Chemical composition

 

 

 

 

 

 

 

CaO ®

51.96*

-

50.00

-

53.20

51.69 -53.20

(Based on

 

MgO ®

1.380

-

3.650

-

1.52

0.79 - 4.05

analysis of

 

TiO2 ®

0.005

-

0.125

-

-

0.011

two

 

Fe2O3 ®

0.1000

 

0.140

-

0.24

0.22 - 0.22

samples)

 

Special features

High in Pyrite and sulphur Develops Pinholes

High in Pyrite and sulphur Develops Pinholes

Iron Impurities

Calcitic marble

Calcitic marble

Calcitic marble

8.

Physical properties

 

 

 

 

 

 

A

Sp. Gravity

2.69

ND

2.70

ND

ND

2.69

B

Water absorption %

0.107%

ND

0.202%

ND

ND

0.200%

9.

Size of Pits

30 m ´ 20 m

30 m ´ 20 m

30 m ´ 30 m

30 m ´ 30 m

30 m ´ 20 m

30 m ´ 20 m

 

 

100 m ´ 100 m

100 m ´ 100 m

100 m ´ 100 m towards North

 

 

25 m ´ 100 m in new mines of Bilu-Mored range

10.

Position of mines with respect to water table

Water table 33-45 m

Quarrying above water table in most of the mines, near Hanuman temple on bye pass road quarrying is below water table.

Approaching water table Depth to water table 45 m.

Fast approaching water table*

Close to water table in most of the mines. Mining  10-15 m below water table

Below water table in most of the mines water level 30 m - 40 m in Kala Nada area deeper in other mines. Mining pits vary in depth from  60 m - 70 m

11.

Generation of waste

High 65%

High 65%

55-60%

50-60%

50-60%

50-60%

 

Recovery

Low 35-40%

Low 35-40% Moderate to high in mines using wire saw

40-45%

35-40%

40%

40-50%

 

 

Poor recovery due to absence of parting Planes Removal of slabs is along fractures, joints etc.

Recovery is better than Borawar Kumhari

Moderate

Moderate

Recovery is more in Bhont,  Ulodi, Gunavati and Chousira, Less in Kala nada, Retdi mines, and Kolha dungri - Bilu-Mored range.

12.

Quality

¬                   poor

®

 

 

 

 

 

 

¬            Kumhari

Quality     ®

Satisfactory to Good

Good

Chuck dungri-very good

Dungri - good

Dungri Adanga-Satisfactory

Ulodi - Chousira, Bhont, Gunavati and Pahad Kua Produce very good quality marble

 

 

Develops pin holes and gives smell of

 

¬ Good for house hold

construction

®

Chausira is best quality white marble

 

 

hydrogen sulphide

not recommended for house hold construction

 

 

 

Dark strips on white back ground is Albeta quality, which is also considered very good quality

13.

Usability of marble

only for slabs

Mainly for slabs; marble of Nahta mines is used for monumental work

 

Mainly for slabs

Mainly for slabs, tables, pillars etc.

Mainly for slabs and tiles.

Mainly for art and crafts, Monuments, temple statues marble used in Tajmahal is from  Pahadkua, Ulodi and Chousira mines.

14.

Price range

 

Rs. 20-30 /sq.ft

Rs. 20-35 /sq.ft

Rs. 30-45 /sq.ft

Rs. 25-50 /sq.ft

Rs. 45-200 /sq.ft

Rs. 40-900 /sq.ft *

 

15.

No. of mines / lease holds***

 

108

67

50

162

441 as per DMG data more than 500 mines as per verbal communication from Makrana Vypar Mandal

          

* Quarrying is at or near water table in most of the mines. General quarry level is 50 m - 70 m.

** Actual lease hold is smaller than 5 m ´ 3 m in old mines (Bapi mines).

1.     Total lease hold area 352.37 Ha (DMG, Makrana)

2.     Communication from Makrana Vypar Mandal

3.     Total number of mines / lease holds is 819 as per DMG, Makrana as on March, 1998.

4.     Total numbers of operating mines - more than 1000 as per verbal Communication from Makrana Vyapar Mandal.

5.     Best quality white marble with 90% whiteness from Chausira mines is sold at a price range from Rs.300/- to 900/- per sq.ft. Brown and grey Albeta

Marble is sold at price ranging from Rs. 90/- to Rs.300/- sq.ft.

 

CONCLUSION

        Significant conclusions emerging out of this study are:

1.   Increase in spread of mining area, waste dumps and built up land is indicated in temporal analysis of visually interpreted aerial photographs of September 1967 and January 1976 and Geocoded satellite immagey of February 1998. This increase is at the expense of agricultural land, open lands, ponds and pasture land over last 20-30 years.

2.   Occurrence of marble in steep dipping parallel bands and small lease holds prevent mechanisation. Due to small and deep mining pits, disposal of waste is not restricted to the excavated area only. Waste dumps dot the mining area throughout from Mata Bhar in the north to Bilu-Mored in the south and from Gunavati in the east to Borawar Kumhari in the west.

3.   Unmechanised mining on small lease holds and blasting results in high waste generation and resource wastage in the area.

4.   Mining muck, over burden dumps and slurry dumps are not segregated in the area. Slurry disposal is done on contract basis due to which contractors dispose of the marble slurry in open lands, agricultural land, ponds and even on road side near the processing plants without giving due regard to aesthetics and pollution aspects.

5.   Designated sites for marble slurry (Pandu) disposal are not properly sited and are insufficient.

6.   Afforestation and compensatory forestry has not been undertaken in the mining area.

7.   No effort has been made for stabilisation of waste dumps. Waste dumps have developed rills and Gullys. Washouts from waste dumps and slurry dumps are contaminating soil and ground water resources in the immediate vicinity of waste dumps. Soil samples show slight increase in Ca, SO4, Na, TiO2 and Mg content of soils in the immediate vicinity of dumps. Ground water samples show appreciable increase in Ca, SO4, NO3, Mg, TDS and SiO2 values of the water samples of mine pit water and slurry laden water.

8.   Kala Nada is a point source of ground water contamination in the area and poses severe threat for the health and hygiene of people living in Makrana and adjoining villages.

9.   Improper mining and non-enforcement of safety rules and mining laws is causing loss of life and public property in the area. Incidents like Chuck dungri railway line collapse can again occur in near future if safety rules are not followed strictly and preventive measures are not taken.

10. Though the Government receives a revenue of thirteen crores rupees per annum from the mining and related activities, there is no improvement in basic civic amenities like roads, good schools, park, potable drinking water supply, hospitals, electricity etc.

11. Complete lack of vegetation screens and indiscriminate dumping of waste is causing air and noise pollution in the core area.

12. Mining and related activities have significant impact on soil, landuse, water, air, noise, flora, fauna, health, safety and aesthetics of the core area, the impacts are marginal or negligible in the buffer zone. However, mining and related activities have major beneficial impacts on socioeconomics of the entire region and Rajasthan state. Mining has appreciable adverse impact on human settlements in the core area and slight beneficial impact on provision of civic amenities in the core area. 

13. Total environmental impact score of mining for the area is (-3875) indicating major injurious impact on environment. Since, mining is location specific activity, major environmental control measures are required to be taken for mitigation of hazards, restoration of natural ecosystem and sustainable development of the mining area. Few remedial measures are suggested for sustainable development of the area.

 
Suggested Remedial Measures

 

Use of natural resources and their transformation into economically valuable commodities has to be sustainable (WCED 1987) otherwise the very base of development will be eroded.  Marble mining at Makrana is a classic example of unscientific mining and improper waste disposal regardless of aesthetics, proper land use practices etc.  Mining and waste disposal practices prevalent in the area need to be reviewed.  Processing waste can be disposed of in abandoned pits and gully erosion areas northeast of Jusri and east of Bidiyad railway station. Segregation of overburden, mine muck, marble slurry and municipal waste dumps is suggested to prevent contamination of ground water and land reclamation and restoration.  Land reclamation is also easier and cheaper if mining waste is segregated. Value of marble depends on its size, whiteness, fine texture and absence or presence of cracks, fractures etc.  It is, therefore, suggested that as far as possible blasting should be avoided and deployment of wire saw machines be encouraged for mining.  Amalgamation of small lease holds and mining on co-operative basis needs to be explored in consultation with mine owners, government representatives and environ-mentalists for sustainable development of the mining area. This will also help in simultaneous reclamation and restoration of mines.  In addition to these remedial measures, vegetation screens all around mining belt, stabilization of overburden dumps, realignment of Howrah-Jodhpur and Makrana-Parbatsar railway lines are suggested for environmental management of the area.

 

REFERENCES

 

BUREAU OF INDIAN STANDARDS, (1969), Specification No. 1130 on Classification of marbles.

DIRECTORATE OF MINES AND GEOLOGY, (2000) : Rajasthan Mineral Bulletin Vo.21, No.4 pp.21-30.

GEOLOGICAL SURVEY OF INDIA, (1997):  Quadrangle Geological map of 45 I

GEOLOGICAL SURVEY OF INDIA, (2001):  Geology and Mineral Resources of Rajasthan, Misc. Publ. No. 30, Pt. 12, 2nd rev. edition.

GOVERNMENT OF RAJASTHAN, (1994):  Marble policy published in Department notification Mines (Gr.II), Gazette extra ordinary October 6, 1994, Jaipur.

INDIAN BUREAU OF MINES, (1993):Market survey Report on Marble MS 19 p.135.

INDIAN BUREAU OF MINES, (1997):  Indian Mineral Year Book Vol. 2, pp 237-243.

NATANI, J.V., (2000): Geoenvironmental impact assessment studies of Makrana Marble mining area, Nagaur district, Rajasthan. Rec. Geol. Surv. Ind. Vol. 133 Pt.7, pp. 64-65.

NATANI, J.V., (2001): Geoenvironmental impact assessment studies of Makrana Marble mining area, Nagaur district, Rajasthan. Rec. Geol. Surv. Ind. Vol. 134 Pt.7, pp 63-64.

NATANI, J.V., (2002): Regional assessment of Marble and calc silicate rocks of Rajasthan.  Rec. Geol. Surv. Ind. Vol. 135 Pt.7, pp 53-55.

PAREEK, H.S., (1984) : Pre-quaternary geology and mineral resources of Rajasthan. Mem. Geol. Surv. Ind. Vol. 115, pp. 1-27.

WORLD COMMISSION ON ENVIRONMENT AND DEVELOPMENT, (1987): Our Common future, Oxford University Press, Oxford, U.K.