Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.0 PROPOSED MINING AND SOURCES OF POLLUTION 2.1 Introduction This chapter deals with the geology of the mining lease area, exploration details, evaluation of the deposit, estimation of reserves, method of mining, machinery, phase wise mineral extraction details, details on infrastructure, various sources of pollution and the control measures. 2.2 Description of the Mines The general and technical details of the mining operations are given in Table-2.1. TABLE-2.1 DESCRIPTION OF MINES Sr. No. I 1 2 Parameter General Mine Features Latitude Longitude Site and its surroundings 3 4 5 Pre mining landuse Distance from proposed refinery Streams / Nallahs 6 Nearest stream / river II 1 2 3 4 5 6 7 8 9 10 11 Mine Technical Features Method of mining Proposed Production from mine lease Expected total Overburden Total ML area Mineable Reserves Extent of mechanization Type of Blasting Type of drilling Power requirement Source of Power Water requirement 12 13 a b C 14 A Water source Waste water Generation Domestic waste Industrial waste Mine water discharge Waste Water Treatment Sanitary waste b 15 Industrial waste Noise Levels VIMTA Labs Limited, Hyderabad Description the 19o18' N to 19o22' N 82o57’ E to 82o59' E in Toposheet 65 I/15 Site is a hillock with plateau top, ground slope varies between 1:40 and 1:5 and at few places slopes are steeper than 1:10. Barren and waste land 16.0-km (Aerial) Nil on plateau top, except a few rain-fed run-off channels Khandabindha nallah, a major tributary of Indravati River (0.5-km, N of plateau bottom) Opencast mechanised mining 3.0 MTPA (Before expansion); 8.5 MTPA (Total after proposed expansion) 153.42 Million Tonnes 1388.74-ha 194.5 Million Tonnes 100% Deep hole blasting with delay detonators Down the hole drilling 3000 kW From CPP of alumina plant 720 m3/d (Before expansion) 2000 m3/d (Total after expansion) San river water 40 m3/d (Total after expansion) 220 m3/d (Total after expansion) Nil The sanitary waste from the mine service yards is treated in Sewage Treatment Plant Vehicle wash water and workshop wastewater will be treated in oil water separator and sent to STP Maintenance of HEMM to keep the noise levels <85 dB(A) C2-11 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution Sr. No. 16 17 18 19 2.3 Parameter Ground vibration Solid waste generation Fire Fighting System Stripping ratio (ore : overburden) Description Within the safe limits Overburden – 6.2 MTPA Adequate fire fighting systems will be provided on all HEMM 1.4 : 1 Geology and Hydrogeology 2.3.1 Physiography Baphlimali plateau forms a part of Eastern Ghat hills. The plateau top is generally flat and the elevation varies from 990-m to 1093-m. The plateau is devoid of vegetation in most part. The ground elevation in the plains is about 750-m. 2.3.2 Existing Drainage The Baphlimali plateau top has a relatively flat relief with slopes towards the fringes of the plateau. The plateau top has no streams or nallahs, except the run-off of rainwater during monsoon. A number of springs originate from the foothills of the plateau at about 100-150m below the plateau top. The streams originating from the foothills of the Baphlimali Plateau have been assessed for its quality and quantity. These streams originating from Baphlimali either join Khandabinda nallah on north or San nallah on the south of the deposit. River Indravati, the main water course in the region, flows in SW direction on the W side of the deposit at a distance of 7.5-km. The Khandabinda nallah, a major tributary of Indravati River, flows at about 0.5-km in N. San nallah is flowing at about 7.5-km in S direction from the plateau. Surface water flow measurements indicate that the flow is gradually decreasing from December to April. Earlier, flow measurements indicate that the flow in these streams decreases further and the minimum flow is observed during first or second week of May. However, the streams are perennial in nature. Quality of both surface water and groundwater is good without high concentration of pollutants. The pre mining surface drainage pattern of the mine lease area is shown in surface map under Figure-2.1. 2.3.3 Geology 2.3.3.1 Regional Geology The lateritisation of the east coast bauxite deposits was developed at the expense of gneisses and schists. The dominant rock assemblage in the region, comprise khondalites (quartz-garnet-potash-feldspar-sillimanite gneisses with or without graphite) and its variants. These are high grade metasediments of argillaceous, arenaceous and calcareous nature. The other group includes charnockites (hypersthene-diopside granulites) and its equivalents, porphyritic granite VIMTA Labs Limited, Hyderabad C2-21 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution gneisses etc. of Precambrian age. The general stratigraphic succession is as follows: Recent alluvium and soil Recent Ferruginous and aluminous laterite and Tertiary bauxite (on hill tops) ------------------------------------Unconformity-----------------------------------Garnetiferous porphyritic granodiorite and Precambrian gneiss with later leuco-granite (Charnockite suite) Garnetiferous quartizite, graphite sillimanite - garnet B quartz gneiss (Khondalite suite) 2.3.3.2 Geology of the Deposit The deposit occupies the crest of Baphlimali Parbat, a hill in the Eastern Ghats. The hill is essentially composed of khondalites with charnockites occurring in the south-eastern part of the hill. The formations have NE-SW trend and steep southeasterly dips of 50-80 degrees. The important characteristics in the profile of Baphlimali deposit are summarised below: Top soil is mostly lateritic in nature varying between 0-2m in thickness and covers almost 50% of the plateau area. The laterite is more ferruginous and siliceous at the top where it is hard and has cloggy, cavernous look. It gradually becomes more soft with depth where it is aluminous in nature grading into bauxite. The clay bearing areas and clayey laterites, occurring on the surface, are marked by growth of dwarf palms. The bauxite shows gradational contact with overlying laterite and has a fairly sharp contact with the underlying partially leached parent rock. Roof of bauxite, due to gradational contact with overlying laterite, is a chemical boundary and thus becomes a function of cut-off grades adopted by the user. Floor of bauxite has a sharp contact with underlying partially lateritised Khondalite (PLK)/partially Kaolinised Khondalite (PKK). The undulations on bauxite floor are rapid and sharp as compared to those on the roof. There are some occurrences of PLK/PKK mixed bauxite and also aluminous laterite patches within the bauxite column as inside waste. The average thickness of overburden and bauxite globally for the deposit is estimated to be 9.84-m and 11.51-m respectively. There is a gradual decrease in hardness and compactness of bauxite from top to bottom. VIMTA Labs Limited, Hyderabad C2-31 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution There are few small patches of no-ore zones (non mineralised areas) which have been confirmed by drilling. These no-ore zones are formed either due to exposures of Khondalite on the surface or due to non-enrichment of alumina in the entire lateritic/ bauxitic column. Geomorphology - Surface Features The laterite cover occupies the crest of the hill between 990-m and 1093-m RL with a relief of about 103-m, Baphlimali is characterised by a relatively flatter profile when compared to other bauxite plateau in the east coast region. The ground slope varies between 1:40 and 1:5. Slopes steeper than 1:10 are rare. Nearly half of the peripheral length of the plateau (29.5 km) is marked by scarps (2-17 m height) with an average of 8-m. The scarps are better developed in the eastern side where the maximum thickness of bauxite has been observed. The scarps are generally aligned sub-parallel to the strike of the formation. The ground slopes do not show any diagnostic relationships with ore characteristics. However, they may be broadly correlated as follows: The surface of the plateau is largely covered with lateritic soil. There are, however, a few impersistent narrow exposures of pisolitic laterite (essentially ferruginous) dissecting the capping at places and a few weathered khondalite exposures restricted to the high topographical zone. Some partially lateritised khondalite patches (PLK) could be seen with laterite exposures. Most of the scarps expose only the partial thickness of the laterite/bauxite column and a few others do expose the PLK/weathered khondalite. Bauxite is considered to have been derived by the in-situ chemical weathering of the khondalites. It occurs as a gently dipping or near horizontal blanket capping over partially lateritised or weathered khondalite. Both laterite and bauxite show relict foliation The average thickness of ore body is arrived at by weighting the thickness of the bauxite zone indicated by exploration points spaced at regular grid intervals against their areas of influence. Narrow discrete partings of non-ore intervening with bauxite have been included in bauxite for practical considerations. Where thickness is so high as to convert the quality of material into non-ore if combined with bauxite, only one subzone, generally the top one, has been accepted as bauxite. The reserves of zone below the non-ore partings have been estimated separately. The various lithounits adopted for the current exercise are as follows: DETAILS OF LITHOTYPES Litho Unit Number 1 2 3 4 5 6 7 Lithology Soil and soil mixed laterite Hard Laterite with very high slilica High silica aluminous laterite Low silica aluminous laterite Bauxite PLK/PKK mixed with bauxite PLK/PKK and Khondalite VIMTA Labs Limited, Hyderabad Thickness Range (m) 0-2 2-5 Average Thickness (m) 0.5 3 2-3 1-2 6-41 Deeper Deeper 2 1 13 C2-41 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution The detailed description of different lithotypes is as follows: Lithounits 1 and 2 essentially form a part of overburden at the top. Lithounit 3 is predominantly occurring as overburden below the lithounit 2. However, there are few occurrences of lithounit 3 within the ore column as inside waste. Lithounit 4 occurs equally as inside waste within ore column and as bottommost layer of overburden just above the ore-roof. Lithounit 5 is typical bauxite and forms more than 90% of the ore column. Lithounit 6 invariably occurs just below the ore column within one to two meter horizon. However, there are few instances of lithounit 6 occurring as inside waste within the ore column. Lithounit 7 is essentially a bottom waste below the lithounit 6 and thus is not significant from point of view of mining/ wining the ore. From the above it is obvious that litho units 1, 2 & 7 are not expected to mix with ore during mining. Thus litho units 3, 4, 5 and 6 are important for defining ore column and mineable column in individual drill holes. 2.4 Exploration and Exploitation Drilling is the most important exploration activity undertaken during this exploration, especially since most of the deposit is covered under capping of soil. The pattern and type of drilling for proving a given deposit depends on the topography, shape, size, extent, compositional variation, attitude of beds and structure of the deposit. Taking these parameters into consideration, scientific drilling was adopted. The lease area has been extensively explored in detail by Geological Survey of India (GSI) (during 1976-77), Mineral Exploration Corporation Limited (MECL) (during 1978-81), INDAL (during 1992) and MECL (during 1998-99) to establish mineral reserves. Details of exploration carried in the lease area are described below: TABLE 2.2 SUMMARY OF TOTAL EXPLORATION WORKS Sr. No. 1 Agency GSI Year 1976-77 2 MECL 1978-81 3 INDAL 1992 4 MECL 1998-99 VIMTA Labs Limited, Hyderabad Summary of Works Drill holes: 52 Meterage : 1445.65 No. Of drill hole samples : 1240 Drill Holes : 530 (504 vertical + 26 inclined) Meterage : 17843.55 (16758.15 vertical + 1085.40 inclined) No. of Samples : 21837 Deep pits : 33 Meterage : 955.40 61 m3 of trenching 341 samples studied for petrology & minerology Moisture and Density determinations Redrilling of 30 holes by vacuum suction located on MECL bore hole points, meterage 792 Resampling of 6 nos. of MECL pits Drill holes : 45 Meterage : 1228 No. of samples : 1209 C2-51 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.4.1 Exploration as done by MECL Based on the resource evaluation studies done by GSI, MECL planned and executed detailed exploration programme at the instance of Govt. of India. The methodology followed by MECL has been described in the following sections. 2.4.1.1 Method of Exploration done by MECL a) Topographical Surveying Triangulation and levelling survey was carried out over the entire bauxite plateau and a network of 26 Triangulation stations was laid down. All GSI bore holes were also connected to these stations. A central axial line and cross-section lines at every 200 m interval (or less in selected areas) were laid from the nearest triangulation station. The survey grid was connected to Survey of India Triangulation Station T-10 at 1093.22 m (Topo Sheet No. 65 I/15). The base plan for geological mapping was developed on 1:2000 in three parts covering the entire plateau top. b) Geological Mapping The detailed geological mapping was done to demarcate: Lithological boundaries; Outcrops of laterite based on visual; Bauxite estimation; Clay estimation; Khondalite (including Kaolinised and partially lateritised khondalites); and Structural features, viz. o Attitudes of foliation in khondalites and relict foliation o Plunges of minor folds Apart from visual examination, limited shallow pitting was also carried out to demarcate contact between bauxite and non-bauxite. c) Drilling Since the experience with wet drilling in other East-Coast Bauxite deposits did not yield acceptable core recovery, conventional rotary dry drilling techniques using tungsten-carbide tipped casing bits (NX in first 5m and BX in the rest) was adopted to ensure full recovery. Core by this method was obtained in the form of powder or chips. Air flush coring method was used in a few cases where hard laterite was encountered particularly in the top layers. A total of 504 Vertical and 26 inclined holes were drilled covering 17,843.38-m drillage. 33 deep pits were also used. The depth of vertical holes ranged from 18.65-m to 55.10-m and depth of inclined holes ranged from 24.50-m to 57.67-m. After studying the lithomaps of pit walls, it was concluded that the bauxite grade revealed in pits is inferior to the ones revealed in corresponding bore holes and this dilution is mainly caused by fluctuations in ore-floor and partly by fluctuation in ore-roof over the areal extent (2.5m x 2.5m) of the pit. VIMTA Labs Limited, Hyderabad C2-61 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.4.1.2 Resource Evaluation by MECL Surface geological studies and voluminous sampling data obtained from bore holes, deep pits, trenches and scarps formed the basis for MECL to determine spatial characteristics of Baphlimali bauxite & overburden and chemistry of bauxite and associated rocks. These were used subsequently in estimating reserves and grades of bauxite. 2.4.1.3 Results of Reserve Estimation by MECL The overall in-situ reserves and grades of Baphlimali bauxite deposit following the above procedure by MECL using chemical cut off at +40% Al 2O3 and -5% SiO2 has been estimated as under: Total surface Area explored: 9.466 km 2 Overburden: Mean Thickness is 9.84-m and Total Quantity is 153.33 MT Bauxite: Mean Thickness is 11.51-m and Total Quantity is 186.43 MT Average Quality of Bauxite: Al2O3 -44.95%; SiO2 -1.9%; Fe2O3 -26.34%; TiO2 2.07%; and LOI -24.19% The surface plan for the mine lease is furnished as Figure-2.1. The geological plan for the lease area applied for renewal on 1:2000 scale is given as Figure2.2. 2.4.2 Geological Sections A total of 41 vertical sections running at right angles to the general strike (N40030'E) of Khondalite were drawn interactively on the graphic screen where for each hole OB column, ore column and their respective grades were displayed. One longitudinal section trending N40030'E was additionally drawn for evaluating the mineral continuity. The geological sections drawn on 1:5000 are shown in Figure-2.3. 2.4.3 Adequacy of Exploration Done Based on the experience of a similar working mine now in operation, it may be concluded that the level of exploration done is adequate for an investment decision at Baphlimali Plateau. This is reflected from the fact that this working mine was drilled at 200-mx200-m to 200-mx400-m grids at the time of investment decision and the working experience has shown broad conformity with subsequent phases of global estimation without any surprises. It is thus clear that the present level of exploration in Baphlimali deposit by MECL provides adequate confidence in taking an investment decision to develop mines for supplying bauxite to the alumina plant, with a consistent quality. VIMTA Labs Limited, Hyderabad C2-71 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution FIGURE-2.1 SURFACE PLAN OF MINE LEASE AREA VIMTA Labs Limited, Hyderabad C2-81 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution FIGURE-2.2 GEOLOGICAL PLAN OF MINE LEASE AREA VIMTA Labs Limited, Hyderabad C2-91 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution FIGURE-2.3(A) GEOLOGICAL LONGITUDINAL SECTIONS OF MINE LEASE VIMTA Labs Limited, Hyderabad C2-101 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution FIGURE-2.3(B) GEOLOGICAL TRANSVERSE SECTIONS OF MINE LEASE VIMTA Labs Limited, Hyderabad C2-111 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.4.4 Future Exploration At the first instance the deposit, as a whole, needs to be covered by 100m grid spacing to generate sufficient information necessary for basic engineering. This permits block-wise estimates for the deposit for blocks of 100-mx100-m with sufficient accuracy, and would help in drawing up an accurate enough mining programme adapted to the deposit characteristics. This step should be followed by a closer grid of say 25-mx25-m in the immediate area of interest to generate short and medium term plans as the project progresses. Smaller grid spacing, can only study a restricted area of the deposit, but with greater accuracy. These should, therefore, be distributed in the areas at least one and a half years ahead of mining faces in order to have advance information before mining takes place in the area. All the future drilling campaigns (Phases I, II & III) will need to be undertaken concurrently at varying paces. No of holes required annually for Phase I & II drilling is 123, based on a time frame of 2 years for Phase I and 5 years for Phase II drilling. Phase III drilling should however be at a much faster pace and should start one and a half years before start of overburden removal. This lead should continue throughout so that advance information is available on small dimension blocks. The annual meterage required to be drilled works out to 3,33,900 m. 2.5 Reserves 2.5.1 Categorisation of Reserves Under UNFC classsification, the total deposit reserves need to be reported under the following eight categories: A Mineral Reserve 1. Proved Mineral reserve (111); 2. Probable Mineral Reserve (121 & 122). B Remaining Resources 1. 2. 3. 4. 5. 6. Feasibility Mineral Resource (211); Prefeasibility Mineral Resource (221 & 222); Measured Mineral Resource (331); Indicated Mineral Resource (332); Inferred Mineral Resource (333); and Reconnaissance Mineral Resource (334). 2.5.2 Estimation of Reserves Geological Reserves Summary of global resources based on 2D kriging is given in Table-2.3. While estimating grades from their accumulation, the kriging variance of the estimated grade is computed as per standard method. VIMTA Labs Limited, Hyderabad C2-121 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution TABLE-2.3 SUMMARY OF RESERVES OF BAPHLIMALI BAUXITE DEPOSITS Over Burden Sector A B C (North) C (South) Total Total Area (Km2) 1.18 4.49 1.65 2.46 9.78 Minera lised Area (Km2) 1.17 4.28 1.57 2.42 9.44 Thickness (m) Tonnage (Millioins) Al2O3 SiO2 % Grade Fe2O3 TiO2 8.23 8.84 8.93 7.64 8.55 18.28 91.64 26.59 35.51 153.42 37.24 36.69 36.96 36.35 36.67 12.06 10.84 6.91 10.76 10.14 Miner alised Area (Km2) 1.17 4.28 1.57 2.42 9.44 Thickness (m) Tonnage (Millioins) Al2O3 SiO2 15.47 13.16 10.67 11.71 12.66 32.58 101.38 30.15 51.01 215.12 44.89 44.90 44.53 45.30 44.95 1.72 1.88 1.82 2.00 1.88 28.97 30.96 34.03 31.38 31.58 1.84 1.98 1.89 1.92 1.95 LOI 19.29 19.05 19.58 19.04 19.14 Bauxite Ore Sector A B C (North) C (South) Total Total Area (Km2) 1.18 4.49 1.65 2.46 9.78 % Grade Fe2O3 TiO2 26.65 26.31 26.78 25.74 26.28 1.96 2.17 2.10 2.14 2.12 LOI 24.24 24.16 24.06 24.27 24.19 A total of 215.12 Million Tonnes of Bauxite reserves (Al 2O3: 44.95%) have been assessed in this mining lease area, with an estimated total overburden of 153.42 MT. Mineable Reserves The geological resources of the deposit have been presented in above sections. The mineable reserves are different from and lower than in-situ reserves and are essentially due to non mining patches, leaving out areas having high stripping ratio (more than 2), loss of ore trapped in unmined peripheral barrier and losses and dilutions during actual mining on account of undulations in floor and roof outlines of bauxite layer. A detailed study has been made to estimate mineable reserves for each block of 25 m x 25 m by modelling the ore body behaviour in terms of roof and floor. The total geological and mineable reserves of the deposit are given in Table-2.4. For the purpose of estimation of reserves, the Tonnage Conversion Factors of 1.8tonne/m3 is applied. The summary of reserves (category wise) is given in Table2.5. TABLE-2.4 MINERAL RESERVES AS ESTIMATED Geological Reserves (MT) 215.12 VIMTA Labs Limited, Hyderabad Mineable Reserves (MT) 194.5 C2-131 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution TABLE-2.5 CATEGORY WISE SUMMARY OF RESERVES Geological Reserves (Million Tonnes) Proved Probable 133.96 ( 111 ) 81.16 (121& 122 ) Mineable Reserves (Million Tonnes) Proved Probable 121.12 ( 111 ) 73.38 (121& 122 ) Note: The figures in the parenthesis are UNFC codes 2.5.3 Anticipated Life of the Mine The anticipated life of the mine is relative and would depend on the quantum of production. The deposit has about 194.5 MT of mineable reserves of bauxite. With the approved mining production of 3.0-MTPA, the life of mine will be about 65-years. Proposed Bauxite excavation is 8.54 MTPA, after the mine got fully developed, i.e., from 9th year of plant operation. During these nine years of production ramp up about 37.54 MT of bauxite will be excavated. Balance 156.96 MT will last for the next 18 years at 8.54 MTPA. Thus the deposit will have a life of 27 years. 2.6 Proposed Mining Technique Mining is proposed to be done by trench method of mining, which is the most suitable for such blanket type deposit with undulating floor. This method is being followed at Panchpatmali bauxite mine of NALCO also and is quite successful for such deposits. The mining technique is described below. 2.6.1 Topsoil/Overburden Removal This operation is done in two phases, the topsoil removal and then lateritic overburden waste excavation. Fertile topsoil wherever occurs is excavated separately by scraping with dozer and the heaps so formed is lifted by loader dumper combinations to be spread on top of backfilled areas for land reclamation. Overburden is to be excavated after loosening by ripper dozer or blasting by a combination of hydraulic shovel, loader, dumper combination. The overburden waste is then backfilled into mined out areas as part of land reclamation scheme. The scheme of backfilling is planned for the entire life of the deposit. During initial three years backfilling is not implemented as mined out area is not available. During this period, the overburden is dumped on southern part of the deposit, and later re-handled gradually from 6th year to 18th year to backfill into mined out areas. The process of rehandling overburden dumps may be expedited so as to complete it before the scheduled period, as and when area for dumping is available. 2.6.2 Bauxite Removal In view of the special bauxite disposition character, the deposit is excavated by trench mining method comprising of a number of parallel trenches with staggered faces. Mining in each trench takes place in two distinct slices. The system of this method is given below. VIMTA Labs Limited, Hyderabad C2-141 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution Mass mining of bauxite top layer (Slice-1) (almost consistent thickness): Bauxite is loosened either by ripper dozer or drilled & blasted. Excavated by hydraulic shovel/loaders, dumpers and transported to the nearest In-pit crusher. The average thickness of this Slice-1 is about 10-m. Selective mining of bottom bauxite (Slice-II) (undulating floor): Bottom bauxite is normally not very hard and does not need any blasting. It can be excavated by a backhoe standing on the bench above. However, wherever it is hard or compact it is loosened through ripping or blasting. The bauxite is then loaded with the help of loader or back-hoe (if space is constrained) and transported by dumpers to the nearest in-pit crusher. The average thickness of this Slice-2 is about 4 to 5-m. Ripper dozer of 770 HP is proposed to be used to rip open the strata and then dozed to form a heap. Various studies carried out on Baphlimali hill have given sufficient indication that 70% of the strata can be loosened by ripper dozer of 770-HP. Very hard patches of strata need to be drilled and blasted, some of the soft areas in selective bottom bauxite can be straight away excavated without either ripping or blasting. 2.6.3 Reclamation Land reclamation envisages backfilling of overburden into mined out areas and topsoil spreading evenly, plantation of local species is proposed after suitable treatment, soil amendments and enrichment of reclaimed land. A sketch indicating the various mining operations in an isometric view is presented in Figure-2.4. The proposed mining techniques to be adopted are given in the Table-2.6. TABLE-2.6 PROPOSED MINING TECHNIQUES TO BE ADOPTED Material Overburden Excavation 70% by ripping 30% by drilling & blasting Rehandling of overburden from external dump - Loading 100% by combination of wheel loader and Front shovel Transport 100% by rear Dumper 100% wheel loader 100% Dumper by Top Bauxite 70% by ripping 30% by drilling and blasting 100% by combination of wheel loader and Front shovel 100% by rear Dumper Bottom Bauxite 30% by ripping 10% by drilling and blasting/balance needs no rock breaking 30%combination of wheel loader and Front shovel 70% by back Hoe 100% Dumper VIMTA Labs Limited, Hyderabad by rear rear C2-151 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution FIGURE-2.4 ISOMETRIC VIEW INDICATING THE VARIOUS MINING OPERATIONS VIMTA Labs Limited, Hyderabad C2-161 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.7 Mine Development and Production Mine production will proceed with the advance of trenches, each trench at different floor level maintaining close to floor. Each trench will have about 80 to 100-m width. The overburden front is mostly planned to have an advance of about 80-100 m ahead of bauxite front, overburden excavation is carried out in single bench of about 8-m on an average, however bauxite excavation is proposed to be carried out in two slices, the top slice (about 10-m thick) will involve unhindered mass-mining, the bottom slice, usually about 4 to 5-m thick, is required to be mined selectively to exclude the non-bauxite high silica zones on the floor. At places with high bauxite thickness, the unhindered mining of bauxite layer may be mined in two slices, so as to leave only about 4 to 5-m or even less for selective mining. The area around first mine cut will be developed to a width of about 1000-m, so as to have about 10-12 trenches advancing parallel to one another. The semimobile crusher will be set up in the central trench so as to have equal distance from the farthest trench. The second crusher will be located during the seventh year of mine operation on the Northern part of the deposit. From 9 th year onwards the two crushers together will deliver full production of 8.5 MTPA of bauxite to the alumina plant. Each crusher will have a capacity of 4.25 MTPA. The mine development involving excavation of overburden and bauxite for initial period of five years is given in Table-2.7. The overburden excavated during the first three years is totally dumped on the southern plateau top. The overburden excavated in the fourth year is partly (2.10-MT) dumped in the designated OB dumps and subsequently backfilled into mined out areas. The year-wise detailed development and production schemes are described in the following sections. TABLE-2.7 YEARLY EXCAVATION OF OVERBURDEN AND BAUXITE Year of operation Overburden Removal (MT) Bauxite Mined (MT) 1 2 3 4 5 6-8 9 2.14 1.00 2.15 3.10 3.02 21.78 6.95 1.24 1.60 3.08 3.70 3.98 23.94 8.50 Grade of Bauxite (%) Al2O3 SiO2 44.21 2.02 44.63 2.10 44.34 2.13 44.43 2.14 44.78 2.12 44.46 2.16 44.28 2.29 Cumulative Bauxite (MT) 1.24 2.84 5.92 9.62 13.60 37.54 46.04 2.7.1 Year-wise Development and Production for the First Five Years of Operation Year-wise detailed mine development drawings and excavation schedules are prepared for the first 5 years. During the first five years 67-ha of area is excavated of which 15-ha area will be backfilled and reclaimed. In the first five years total of 11.41 MT of overburden will be excavated and during the same period 13.60 MT of bauxite will also be excavated. Conceptual mine development drawings at the end of 5th year of operations is given in Figure-2.5. VIMTA Labs Limited, Hyderabad C2-171 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.7.1.1 Mine Development during First Year During first year, apart from opening of the deposit, various construction activities of buildings such as office, workshop, other facilities area, access road, electrical transmission line and distribution network, water pumping, supply, storage and distribution etc will be completed. During this period, 2.14 MT of overburden will be excavated from an area of 14-ha and the overburden so excavated will be dumped in a designated area on the southern part of the plateau top. This will expose about 3.0 MT of bauxite for excavation from different mine faces. Incidental bauxite that will be excavated during the first year will be 1.24 MT, which will be stocked close to the proposed Semi Mobile Crusher. During this period a Semi-Mobile Crusher also will be installed at the floor of bottom bauxite such that the hopper level and the floor of top bauxite are at the same level. 2.7.1.2 Mine Development during Second Year The second year of mine development coincides with the Alumina plant commissioning. Excavation is carried out around the initial mine opening during the second year. The quantum of bauxite excavation during second year will be 1.6-MT. This, together with the bauxite stockpiled during the first year (1.24-MT) totaling to 2.84-MT, will be crushed and conveyed to Alumina plant through a long distance conveyor. The overburden excavated during second year will be 1.00-MT with mine fronts advancing westwards. The overburden excavated is planned to be dumped as in the first year on the southern part of the plateau top since, sufficient mined out area is still not available for backfilling of overburden. Additional 7.0-ha area is exposed during the second year totaling to 21-ha (including 14-ha of the first year). 2.7.1.3 Mine Development during Third Year By this period, the Mine will be sufficiently developed to excavate the desired capacity of bauxite. Excavation and mine advancement progress towards west in parallel trenches following the bauxite floor. The quantum of bauxite excavation during the third year is 3.08-MT, which will be crushed and conveyed to Alumina plant through the long distance conveyor. The overburden excavated during the third year will be 2.15-MT with mine fronts advancing westwards. The overburden excavated is planned to be dumped as in the earlier years on the southern part of the plateau top since, sufficient mined out area is still not available for backfilling of overburden. Additional 14-ha area is exposed during the third year totaling to 35-ha (including 21-ha of the first two years). VIMTA Labs Limited, Hyderabad C2-181 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.7.1.4 Mine Development during Fourth Year Excavation and mine advancement continues in parallel trenches towards west following the bauxite floor. The quantum of bauxite excavation during the fourth year is 3.70-MT, which will be crushed and conveyed to Alumina plant through the long distance conveyor. The overburden excavated during the fourth year will be 3.10-MT with mine fronts advancing westwards. The overburden excavated is planned to be dumped as in the earlier years on the southern part of the plateau top. However, during the later part of fourth year sufficient bottom bauxite has been excavated and mined out area is available for backfilling. Thus, the overburden excavated from then onwards will be backfilled into mined out areas. Additional 19-ha area is exposed during the fourth year totaling to 54-ha (including 35-ha of the first three years). Land reclamation of mined out area by backfilling is carried out over an area of 5-ha during the fourth year. 2.7.1.5 Mine Development during Fifth Year Excavation and mine advancement continues in parallel trenches towards West following the bauxite floor. The quantum of bauxite excavation during the fifth year is 3.98-MT that will be crushed and conveyed to Alumina plant through the long distance conveyor. The overburden excavated during the fifth year will be 3.02-MT with mine fronts advancing westwards. The overburden excavated is planned to be dumped for backfilling into mined out areas available after the excavation of bottom bauxite. Additional 13-ha area is exposed during the fifth year totaling to 67-ha (including 54-ha of the first four years). Land reclamation of mined out area by backfilling is carried out over an area of 10-ha during the fifth year, thus cumulative area reclaimed at the end of fifth year will be 15-ha. 2.7.2 Proposed Rate of Production, when mine is Fully-Developed The proposed rate of production of the mine, when the mine is fully developed is 8.5-MTPA of bauxite. The bauxite mine production will increase from the initial 1.24-MTPA to 8.5-MTPA during the 9th year to suit the requirement of alumina plant. The Semi Mobile Crusher Plant–I (SMCP-I), which is designed for production of 4.25-MTPA and is commissioned during second year, will be in the central part. To cater to the increase of bauxite excavation beyond 4.25-MTPA, a second Semi Mobile Crusher Plant–II (SMCP-II) of similar type and capacity is planned and commissioned on the northern part of the deposit, during the seventh year. During the seventh year the mined out area is sufficient to re-handle the overburden from OB Dumps and backfill into the mined out area around SMCP–I, in addition the overburden excavated around the SMCP–II area on the northern part will also be backfilled into the area available around SMCP–I. VIMTA Labs Limited, Hyderabad C2-191 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution In subsequent years, the bauxite excavation from northern part will further increase and in the ninth year both the working areas near the two SMCPs will be producing 8.5-MTPA of bauxite, simultaneously excavating about 7.0 MTPA of overburden. 2.7.3 Conceptual Production Plan for Tenth Year Onwards Mine development/excavation will be stabilized from 9 th year onwards to excavate 8.5-MTPA of bauxite. Mine Closure plan at 27th year of working is enclosed as Figure-2.6. The mined out area corresponding to Crusher-I will initially advance westwards and then towards south. Accordingly, the crusher is shifted to a location on the Southern part of the plateau. Crusher-I will thus be handling all bauxite in Central, Eastern and Southern side of plateau and Crusher II will be handling all bauxite on the Northern and Western part of the plateau. Due care has been taken during mine planning for proper blending from both mining areas to meet the plant feed grade of bauxite. Year wise Mine plans prepared indicate the area excavated in sequence for overburden excavation, mass mining (of top bauxite), selective mining (of bottom bauxite) and area backfilled by overburden waste. The block krigged values provide data on estimates of overburden thickness, bauxite thickness, quantity, its grade etc for each block of 25-mx25-m. Almost equal quantity of bauxite needs to be excavated from both the mining areas, depending on quality of each 25-mx25-m blocks, areas are selected for mining each year in a sequence so that the required plant feed grade is met. VIMTA Labs Limited, Hyderabad C2-201 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution FIGURE-2.5 MINE DEVELOPMENT PLAN AT THE END OF FIFTH YEAR OF OPERATION VIMTA Labs Limited, Hyderabad C2-211 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution FIGURE-2.6 MINE CLOSURE PLAN VIMTA Labs Limited, Hyderabad C2-221 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.8 Equipment for Ripping, Dozing, Drilling, Loading and Transportation 2.8.1 Mining Equipment The mining will be done with 100% mechanized opencast mining. Proposed mining equipment along with other auxiliary equipment are presented in Table2.8. TABLE-2.8 LIST OF MINING EQUIPMENT Sr. No. Description Capacity No. of Units Existing After Approved Proposed Capacity Expansion (3.0 MTPA) (8.5 MTPA) 2 6 1 Ripper Dozer 770 HP 2 Rotary Drills 2 3 3 Rear Dumpers 150-165 mm 85 T 50T(16) 12 4 11.0 m3 4(4.2m3) 2 5 6 Hydraulic front shovels Front end loader Hydraulic Back Hoes 11.5 m3 11.0 m3 2(5.5m3) -- 3 1 7 Hydraulic Back Hoe 3.2 m3 2 1 8 Track Dozers/bull dozers 320 HP 2(250-300HP) 4 9 wheel dozer 300 HP 1 2 10 Motor Grader 300 HP 1(150HP) 2 11 Water Sprinkler 16 KL 2(28KL) 4 12 Vibratory Compactor 10 T 1 1 13 Mobile Hydraulic Rock Breaker 15-20T 1(100HP) 1 Remarks For excavating overburden, bauxite For Blast hole drilling and production For hauling ore from mine faces to crusher Loading of top bauxite Loading of top bauxite Loading of bottom bauxite Loading of bottom bauxite from constrained areas road maintenance, stockpile handling, levelling in backfill areas etc maintenance of haul roads, ramps and service road maintenance of roads and connecting ramps sprinkling on haul roads and other dust prone areas consolidation on haul roads To break large boulders 2.8.2 Ripping and Dozing Equipment As explained earlier sections, ripper dozer will be deployed in conjunction with wheel loader/Hydraulic Front shovel at overburden, top bauxite and bottom bauxite benches. Based on the hourly ripping and dozing capacity of 470-tph for Baphlimali bauxites using 770-HP class of ripper dozers six number of ripper dozers required have been computed. 2.8.3 Drilling Equipment A drilling pattern of 5m x 4.5m has been proposed and an effective drilling rate of VIMTA Labs Limited, Hyderabad C2-231 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 15 m/h has been assumed for arriving at number of drills. Based on the annual tonnage to be handled by drilling equipment, 3 Nos of 150-165 mm dia drills will be required. One drill is proposed to have standard mast height for deployment in bottom bauxite and other drill of single pass-tall mast type for drilling in overburden and top bauxite. This, however, will be further reviewed at implementation stage, when rippability of the deposit is better understood and firmly quantified. 2.8.4 Sizing of Loading/Hauling Equipment The choice on size of loading and hauling equipment is primarily done by considering the quantum of material handling. Total of bauxite and overburden to be handled is about 15.0-MTPA. A mine with such high material handling capacity has to choose the mining equipment adequately so that too many work fronts are not required to be operated. 2.9 Blasting Details Approximately, 30% of the excavation of top bauxite and overburden, and 70% bottom bauxite, which cannot be dislodged by the ripper, will be drilled and blasted. For effective blasting of the strata, explosive is required to be kept suitably for some amount of confinement. Therefore, it is to be kept within drill holes and after proper stemming and tamping, the explosive will be detonated for explosion. 2.9.1 Blasting Procedure A maximum of 10-m deep blast hole will be formed by the help of Rotary drill of 150 mm diameter and an amount of 70-kg explosive will be loaded per hole. The stemming length of blast hole is proposed at 2.75-m and the balance is for explosive column. The ratio of high explosive to AFNO has been kept at 1:3. The explosives column is to be blasted under “V” type blasting pattern initiated by detonator fuse, detonating etc. 2.9.2 Blasting Hours Atmosphere is hot during day time and comparatively cold in evening hours. In hot atmosphere, instantaneous emitted dust particles from blasting are supposed to spread over a large area than cold atmosphere. Therefore, blasting hours will be restricted to noon hours i.e., 12 noon at 2 pm. 2.9.3 Broad Blasting Parameters Burden : Burden is the perpendicular distance form the hole to the nearest free face in the direction in which the displacement is required to achieve the maximum effect of explosive, the burden is required between 20-50% of the bench height. For Baphlimali bauxite deposit, 45% is considered to be the most optimum figure for medium hard rock, which is also based on field practice of other bauxite mines in the Orissa state. 4.5-m of burden will be provided. VIMTA Labs Limited, Hyderabad C2-241 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution Spacing: Spacing is the distance between individual drill hopes. It normally varies between 1.0-1.3 times of burden. Depending upon the nature of the rock, degree of fragmentation required and method of initiation, spacing is proposed to be kept at 1.1 times of burden. A spacing of 5.0-m will be maintained. Sub-Grade Drilling: To prevent the formation of toe on the bench floor, it is necessary to drill a certain depth more than the height of the bench and this additional drilling, generally called as sub-grade drilling and normally varies within 8-10% of the bench height. Stemming Length: Increase in stemming length, decreases fly rock and noise but increases ground vibration level. For the area under reference, stemming length is proposed at 20 times of the diameter where compressive strength of rock is approximately 400 kg/cm2. Delay Interval: Minimum delay interval between holes will be kept at 4.5-m per meter of burden. The broad blasting parameters for the area are summarized in Table-2.9. TABLE-2.9 SUMMARY OF BLASTING PARAMETERS Parameters Bench height (m) Burden Spacing Sub-grade drilling Depth of the Blast hole Delay interval (minimum) Stemming Length Explosive column length High explosive column ANFO column Material factor Loosening of rock mass per hole Details 8 to 10-m 4.5 m 5.0-m 1.0-m 11.0-m 25.0-m 2.75 m 8.25-m 2.25 m 6.0 m 1.8 t/cum Bench Height x Burden x spacing= 9 x 4.5 x 5.0 = 202.5 cu.m = 202.5 x 1.8 = 365 T 2.9.4 Type of Explosives The most common type of explosives, which are readily available will be used in the mine. The explosives will be: 1. 2. Nitroglycerine based gelatinous explosives; and Ammonium Nitrate Fuel Oil mixture (AFNO). AFNO is an explosive formed by ammonium nitrate (94.0%) with diesel (6.0%) as diesel oil. Ammonium nitrate is easy to handle and stable. It will be mixed with diesel oil at site to produce the explosive mixture just prior to blasting. Combination of these two types of explosives will be best suitable for effective VIMTA Labs Limited, Hyderabad C2-251 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution blasting in the area. The annual consumption of explosives is given in Table2.10. TABLE-2.10 ANNUAL EXPLOSIVE CONSUMPTION Details Ammonium Nitrate (AN) Diesel Oil/Fuel Oil (FO) High explosive Detonating fuse Ordinary detonators Safety fuse Detonating relays Quantity 540 tonnes 40 KL 190 tonnes 220000 m 700 Nos. 2100 m 4125 Nos. 2.9.5 Storage of Explosives Proper storage of explosives and accessories is important: To ensure that these materials are kept out of the hands of unauthorized persons (including anti-social elements); To reduce the hazards of accidental explosions (due to unsafe and wrong handling);and To maintain them in good condition for use. The capacity for storage to be provided will depend on estimated rate of consumption of explosives. The magazine will be located at SW lobe of central part of plateau. The explosives will be stored in approved magazines, licensed by Controller of Explosives, Nagpur. In addition, permission will be taken from Chief Controller to use ANFO in the mines. The explosives will be transported using explosive van of 10-T capacity under the supervision of a competent person. Ammonium nitrate is mixed with diesel oil with strictly safety precautions under the supervision of competent person. All safety Rules and Regulations are followed while storing and transportation of explosives. The magazine to store the explosives will have a capacity of 25-tonnes. 2.10 Bauxite Crushing and Transportation 2.10.1 Crushing The ROM bauxite needs primary crushing at the mine before transportation to the alumina plant at Doragurha. It is proposed to have conveyor transport for Baphlimali bauxite plateau. Primary crushing is necessary at the mine, while the ROM bauxite is likely to have a size of 1000 mm. The crushing system during initial years will consists of one Semi Mobile Crusher (SMC-I) with a capacity of 4.25 MTPA. Later, during the 7th year of mining operations, a second Semi Mobile Crusher (SMC-II) with same capacity and type will be installed on the northern plateau. Thus, 8.5-MTPA of Bauxite to alumina VIMTA Labs Limited, Hyderabad C2-261 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution plant will be mined, crushed and transported, considering alumina plants average requirement of 7,08,332 tonne/month. 2.10.2 Crushing System The flat topography of Baphlimali Plateau with its large areal extent suggests the use of a crushing system which moves with the advancing mining faces. It was therefore decided to make a comparison of fixed Vs mobile types of crushing systems and it is proposed to use Semi Mobile Crushing Plant (SMCP), to have advantages of mobility of system. Semi-mobile Crushing Plant (SMCP) Each SMCP consists of the following main equipments: 200 tonne capacity receiving hopper; Apron feeder whose speed can be adjusted to control feed rate to the plant, based on feed rate from mine; Toothed double roll crusherl Collecting belt conveyor to receive crushed ore, and feeding to bridge conveyor whose length is to be adjusted based on the position of semi-mobile crushing plant; and Shiftable/ Extendable conveyor from SMCP to loading station. The crushing equipment will be installed on a structure which is rendered mobile by mounting on skids. 2.10.2.1 Description of SMCP The description given here covers the system from ROM hopper to discharge end of bridge conveyor for transporting crushed bauxite to loading station. The ROM bauxite from mine is hauled by dumpers (85-T class) and discharged to ROM Hopper. The inside of the hopper is lined with rails all around to withstand impact/wear caused by discharge of bauxite boulders. In case larger/oversize boulders (+1000 mm) are also dumped in to the hopper, these are likely to get stuck at discharge point of hopper and may block the feed to Apron feeder/crusher. A fixed type Rock breaker is provided at the crusher hopper to break such boulders on Apron feeder and thus ensure free flow of bauxite to primary crusher. However, mine will ensure that no oversize boulders of bauxite are fed to the plant. Water sprinkler arrangement is provided to suppress the dust generated around the crusher area. Apron Feeder below the ROM hopper is of variable speed type and its speed is adjusted to maintain uniform flow to Primary crusher based on feeding rate of bauxite from mine. The Apron feeder is of robust construction and can withstand impact of large boulders of bauxite discharged by dumpers from a height, when the hopper is empty. The Primary Toothed Roll Crusher has a gap setting of 150-mm between the rolls during normal operation. However, this gap can be adjusted from 50-mm to 150mm. The rolls are fitted with replaceable wear-resistant teeth. The crusher VIMTA Labs Limited, Hyderabad C2-271 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution reduces the size of bauxite from ‘D85’ of ‘-800mm’ to ‘D85’ of ‘-150mm’. Toothed double roll crusher discharges the crushed bauxite to belt conveyor, which in turn feeds to bridge conveyor. Bag filter type dust collecting system mounted on belt conveyor will collect dust generated by discharge of crushed bauxite on it. An EOT crane of 30/5 T capacity is provided for maintenance of equipment. The equipment mentioned above except the bridge conveyor will be installed on a structure rendered mobile by mounting on skids. Each crusher will operate at 780 tph, but the crushers will be designed at 950 tph. Thus both crushers together will operate at 1560 tph and will be designed for maximum capacity of 1900 tph. The design margin is kept 20% higher to obtain an average capacity of 1560 tph, which is required to meet the plant feed requirements. 2.10.3 Bauxite Transportation to Alumina Refinery Based on various alternative modes of bauxite transport, it is proposed to adopt transportation by single flight (without any transfer points in between) covered conveyor from mine to plant. The conveyor is planned for a carrying capacity of 1560 TPH operating in three shifts per day and with 304 effective days of operations in a year. The conveyor starts from the Semi mobile crusher located on Baphlimali hill and is routed downhill over a distance of about 20-km to the storage yard at the alumina refinery. The conveyor connects loading point (altitude 1,000m) on the plateau top with transfer tower-I (Angle Station) of Alumina plant at an altitude of 800-m. It would follow the most favourable path determined by topographical maps and survey of the region. 2.11 Mining Details 2.11.1 Mine Environment The post mining configuration of the mining area will appear like a bowl shape surrounded on all side by high walls. The mined out areas will largely be filled by the over burden waste. Post mining operations, the profile of the plateau will be changed and the plateau top will be lowered by 10 to 12-m. 2.11.2 Mine Drainage One rain fed runoff is passing along the centre of southern part of the plateau. Two smaller runoff streams are also passing through the plateau. These exist only during monsoon season only and are not perennial sources. During mining operations, the runoff stream will be initially diverted eastwards and later, the runoff stream will not be in existence. Some other streams and rills originating from the foothills of the Baphlimali Plateau either join Khandabinda nallah on north or San nallah on the south of the deposit. These will not be disturbed during the mining operations. Groundwater level is at about 100 to 150-m below the plateau top. It is assessed that the groundwater table is not likely to be intercepted during the mining VIMTA Labs Limited, Hyderabad C2-281 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution operations up to bauxite-bottom, as the mining operations will be restricted to only 25 to 30-m. In addition to the mined out area being backfilled, parts of these areas are proposed to be used as temporary water storage reservoirs to tackle direct precipitation of rainwater in the active mining area. The floor of bottom bauxite is not flat and has varying slopes on which the reservoirs are to be built. These reservoirs will have a limited capacity and may be considered as short term settling ponds for rainwater. The water stored in these reservoirs is most likely to seep through the sub-stratum, which is sufficiently porous and water table is much below the plateau top. Hence, further handling of the accumulated water is not envisaged. 2.11.3 Exploitation and Utilization of Mineral Maximum conservation and optimum utilization of mineral is the mission of the mines management. The mine is captive to the Utkal Alumina Refinery and therefore, entire mined out mineral will be consumed in manufacture of alumina at the refinery site. 2.11.4 Waste and Sub-Grade Mineral Management The lateritic overburden waste overlying the bauxite layer on plateau top has an average thickness of about 8.0-m. The mining scheme envisages removal of overburden waste and to use it for backfilling mined-out areas after bauxite excavation in that area. When the mine is fully developed to produce 8.5 Million TPA of bauxite, about 6.2 million TPA of overburden is required to be excavated. This overburden will be dumped evenly throughout the mined out area, so as to regain the earlier topography. The overburden excavated during the initial years of mining needs to be stored outside the active mining area, but within ML area only, until sufficient area is made available for backfilling. As per the mining scheme proposed, backfilling area is available from the fourth year. The quantity of overburden excavated prior to commencement of backfilling will be about 7.39-MT, which needs to be dumped/ stored outside active mining area (in ML area). In order to facilitate rehandling of OB storage area later and from aesthetics point of view, it is proposed to limit the height of these initial dumps to a maximum of 10-m. This will require an area of about 50-ha, considering the compacted density of overburden at 1.65 t/m3. (compaction to about 80% of loose density). The most suitable location for these overburden dumps is found to be on the southern part of the plateau. This location has been selected because of availability of sufficiently large area taking into account the direction of mine advance, and the lead for rehandling and backfilling into mined out areas. The overburden dumping is planned in two dumps leaving sufficient space in between to allow the water to flow along its natural course, as there is a rain fed drainage passing along the centre of southern part of the plateau. VIMTA Labs Limited, Hyderabad C2-291 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.12 Reclamation and Afforestation Programme 2.12.1 Reclamation It will not be possible to entirely restore the mined out land to its pre mining natural conditions. It is envisaged to reclaim the mines once the available reserves are exhausted suitably by way of plantation, creation of water reservoir etc. Reclamation of mined out land is necessary for restoring the aesthetic beauty of the area and also for putting the land back to better use. The basic scheme for backfilling of overburden into mined out areas shall be to regain the earlier surface profile, as far as possible. However, the void created by the removal of bauxite layer cannot be entirely compensated by the dumping of overburden and there is a likelihood of the topographic level going down on an average by 10-m. The aspect of varying thickness of excavation is taken into account while computing the amount of overburden backfilled. The total tonnage of overburden to be accommodated in each block of 25m x 25m is estimated from the area available for backfilling and the combined excavation thickness of bauxite and overburden in each block, using the tonnage factor of 1.65-t/m3 for compacted overburden. Backfilling is carried out upto the mine boundary and peripheral edge, leaving reservoirs at places where the depth of excavation is high. Direct filling from OB front will resume from 4th year and rehandling from initial overburden dumps will resume from 7th year onwards. Topsoil would be utilised for intensive plantation and greenbelt development in the non- mineral bearing areas, along haul roads, ultimate limit of benches and all along the plateau periphery. The overburden stored on the southern part of the plateau is envisaged to be excavated gradually from the 7th year of mining upto the 18th year and backfilled into mined out areas. Thus, at the end of 18 th year, all the overburden from these dumps shall have been cleared. The re-handling from OB storage area has been planned as a gradual process considering the area available for backfilling. Apart from the above measures, entire overburden generated from the 7 th year onwards will be utilised for concurrent backfilling. 2.12.2 Afforestation Worked out pits would be suitably reclaimed by way of plantation and afforestation. Plantation and greenery development will also taken up along lease periphery, Plateau periphery, along haul roads and also in patches of area identified for the purpose. For re-vegetation, plants and saplings as per soil characteristics and site conditions are being selected in consultation with forest department. In order to facilitate the proper growth of vegetation, suitable measures like preparation of seed bed with suitable amount of fertilizers and treatment with mulches have also been taken up. Vegetation cover around the mine workings helps in dust control, enhancement of aesthetic beauty, minimising run off and reducing noise. VIMTA Labs Limited, Hyderabad C2-301 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution The afforestation will be carried out along the periphery of the lease in safety zone, which will be of 15-m wide. Afforestation will also be carried out in reclamation areas. The plantation, which is not surviving, shall be replanted periodically prior to rainy season. The density of plantations will be about 1500 to 2500 saplings per hectare. The afforestation program proposed is as given in Table-2.11. TABLE-2.11 AFFORESTATION PROGRAMME Period At the At the At the At the At the At the Total end end end end end end of of of of of of 5th year 10th year 15th year 20th year 25th year mine life Backfilled and Reclaimed Area (ha) Number of saplings 15.0 100 100 100 100 185 600 30000 200000 200000 200000 200000 370000 1200000 Greenbelt along Periphery of ML (Safety Zone) Area No. (ha) saplings 6.0 12000 8.75 14000 8.75 14000 8.75 14000 8.75 14000 41.0 14000 41.0 82000 Total Plantation 42000 214000 214000 214000 214000 384000 1282000 2.12.3 Land Use Pattern The present land use pattern in the lease area (prior to commencement of mining operations) comprised of waste / barren land. Presently, the land is not is used for any purposes. The details of the land use at various stages of the mining operations are given in Table-2.12. TABLE-2.12 LANDUSE PATTERN IN MINE LEASE AREA Sr. No. Details 1 Area excavated or in active mining Storage for topsoil Storage for overburden Mineral storage Infrastructure Roads & Conveyor Railways Tailing Pond Greenbelt including green cover in Open Lands Township area Others (Explosive magazine) Open / Vacant / undisturbed Land Reclaimed area of mined out area TOTAL (Excluding Sr. No. 13) 2 3 4 5 6 7 8 9 10 11 12 13 Existing Land Use - Area (ha) After 5 After 10 After 15 Years Years Years 67.0 277.0 487.0 At the end of Mine Life 850.0 - -* 50.0 1.0 11.0 10.0 6.0 -* 50.0 1.0 11.0 10.0 14.75 -* 50.0 1.0 11.0 10.0 23.5 -* 0.0 1.0 11.0 10.0 41.0 1388.74 0.5 1243.24 0.5 1024.49 0.5 805.74 0.5 475.24 - 15.0 115.0 215.0 600.0 1388.74 1388.74 1388.74 1388.74 1388.74 Note: *: Topsoil will be stored within the area to be excavated and concurrently used for reclamation of the back-filled area. Accordingly, it is not quantified separately. VIMTA Labs Limited, Hyderabad C2-311 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.13 Mine Closure Plan Since, this is a proposal prior to opening up of the mine this is a Progressive Mine Closure Plan and is described in the following sections. 2.13.1 Mined Out Land It is proposed to reclaim the mined out area by backfilling of overburden waste in the mined out area in a progressively sequential and scientific manner over the life of the mine as depicted in year-wise mine development plans and mine closure plan. In addition, the reclaimed land will be planted with native species, so as to bring the original flora and & fauna back. This will be done in the following manner: Dump the overburden into mined out area in a layered manner; Doze it to make it even or sloping as per earlier topography; Cover it with fertile topsoil; and Plantation on top. This is considered as the most accepted and environment friendly manner of disposal of overburden and reclaiming the mined out land. Post plantation practices such as preparation of tree basins, partial trimming, plant protection from insect & pest attacks, application of fertilisers & manures to fulfil its nutrition requirements etc would be regularly taken up. In addition to above, the practice of bio mass creation within plantation shall also be taken up to enrich the soil by the nitrogen fixation. Manure would be provided by dried up bio-mass decomposition etc. The summarised account of reclamation is given in Table-2.13. TABLE-2.13 THE SUMMARISED ACCOUNT OF RECLAMATION Year of Working 1 2 3 4 5 6-10 11-15 16-20 20– Mine Life Total Opened up Area (ha) 14.0 7.0 14.0 19.0 13.0 210.0 210.0 210.0 153.0 850.0 Reclaimed Area (ha) 0.0 0.0 0.0 5.0 10.0 100.0 100.0 100.0 285.0 600.0 2.13.2 Waste Management At Baphlimali bauxite deposit total waste rock generated over the life of the mine is 139.23 MT while the quantity of bauxite mined is 194.5 MT. The waste rock is lateritic in nature and is not known to contain any toxic or hazardous chemicals. The overburden waste is proposed to be backfilled into mined out areas to reclaim the land as described earlier. VIMTA Labs Limited, Hyderabad C2-321 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.13.3 Topsoil Management In view of the importance of topsoil in maintaining the fertility of the land, during mining, the topsoil (wherever it occurs) will be first scraped out and preserved separately. The total quantity of the topsoil in the ML area is estimated as 30 MT. After systematic backfilling of overburden waste into mined out areas, the following measures are proposed: Topsoil spreading evenly over the backfilled areas to regain the fertility of the land; Suitable soil treatment and making it worthy for plantation; and Plantation in the reclaimed areas. 2.13.4 Tailing Dam Management As no beneficiation of mineral is envisaged at mines, no tailing dam is envisaged. 2.13.5 Infrastructure The mine is proposed to have two Semi Mobile in pit Primary Crushing units near the mine working faces. The Alumina plant, which is located on SE of the deposit, is connected to the mine by a 20-km long single flight long distance conveyor for transport of bauxite from the mine. The Explosive Magazine is located on one of the lobe of the plateau on the South Western side. The various other mine facilities (Site Services) provided at plateau top for the smooth operation. These facilities are located in an area of about 11-ha at the eastern end of the plateau at 1010-m elevation. The approach road to the mine on hilltop from the alumina plant is routed along the eastern foothill towards the south eastern side of the hill gradually. In view of the continuous plantation and concurrent reclamation of the mined out area, on mine closure the entire mining complex would turn out with greenery of plantation all around the plateau top interspersed with a number of small reservoir ponds all over. It is envisaged that when the mine is closed, most of the structures will have out lived their life. Any structure, which is not required at the site after the mine closure can be dismantled or relocated to other group company sites for further use. Some of the civil structures will be dismantled and razed to the ground. 2.13.6 Disposal of Mining Machinery Most of the mining machinery would have reached to end of their useful life. However, some of the equipments, which are still in operating condition, are proposed to be shifted to other locations or they will be sold off as second hand mining equipment. 2.14 Mine Support Facilities and Utilities The following facilities are proposed at Baphlimali plateau top: VIMTA Labs Limited, Hyderabad C2-331 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution Mine office for general administration; Workshop and Stores (servicing and repairing shop); Explosive Magazine; Ammonium Nitrate Storage; Mixing shed for ANFO; Pit Office including field maintenance shed; Rest shelters; Fuel filling station and lubricant store; Fire Station & First-Aid Station; Sample Preparation Station; Canteen; Training Centre; Main Receiving Sub-station; Environment, Occupational health & Safety; Water Storage, treatment and pumping facilities; Check-post & Rest rooms; Storm water drains; Magazine (for storage of High Explosives); Toilet facilities; First aid station (s); and Weigh bridge. The facilities will be located at hill top on one of the extension lobes of eastern periphery of the plateau, approximately midway between its northern and southern extremities. This lobe is nearly devoid of bauxite mineralisation, and is separated from the main mining area by a buffer of trees. All the facilities have been located within an area of 11-ha. 2.14.1 Access Road The access road to mines starts from Tikiri-Kashipur road junction via refinery site and Dongasil village upto mine top. From Kupakhal situated just downhill of Baphlimali deposit, the road rises along the eastern escarpment to the entry gate of facility area at 1010-m contour. The road also passes close to the water intake point at Katkhal crossing the San River. The road distance from mines top to the alumina plant is approximately 30-km. The total length upto Tikri-Kashipur Road junction is 37-km of which about 14-km will be totally new construction. This road will have a width of 9.0-m. 2.14.2 Work Shop Servicing and Repair Shop A floor area of approximately 500-m2 covered by the structural steel construction will house for servicing and repair centre. 2.14.3 Fire Station/First Aid Room A fire station with all the fire fighting equipment and a fire tender will be stationed at the mines facilities as per the safety norms. Integrated in the same building a first aid room with attending doctor will be stationed. VIMTA Labs Limited, Hyderabad C2-341 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.14.4 Electric Power Since the mine will have mostly diesel operated mobile mining equipment, the electrical load will be mainly on account of crusher system, workshop equipment, mine lighting, office lighting and miscellaneous loads like water pumping etc. The electric power required for mine to plant long distance conveyor has been included in the alumina plant electric load. The power required for the Baphlimali mine for all the above activities after expansion to 8.5-MTPA will be about 3000KW. The power requirement at 3.0-MTPA production level is estimated as about 1000-KW The power will be drawn at 33 KV from alumina plant over a distance of 20-km and received at electric sub-station located near conveyor loading station. Apart from this, the mines will have a 500 KVA DG set for emergency power supply to cater to various lighting loads and the computer centre. 2.14.5 Fuel Requirement Since most of the mine equipment are mobile equipment, they operate on Diesel (High Speed Diesel). Diesel will be required for the following areas: Mobile mining equipment; As Fuel Oil for ANFO Explosive; and Emergency diesel generating set. It is estimated that the daily diesel consumption would be about 32-KL per day (after expansion to 8.5-MTPA) for which a storage of 2X70 KL above ground steel tanks have been envisaged. 2.14.6 Water Supply/Requirement Industrial water is required for mining operations/establishment mainly for sprinkling on haulage roads and at faces for suppression of dust. Water is also required for vehicle washing and servicing utilities for equipment and also for green cover development. Total water requirement after expansion to 8.5-MTPA is estimated to be about 2000-m3/day. Water will be sourced from San river water at Kathkal site. The break-up of water requirement for different units is given in Table-2.14. TABLE-2.14 WATER REQUIREMENT FOR MINES Purpose Dust suppression / sprinkling on haul roads Vehicle washing Workshop Domestic water Green cover development Miscellaneous & others Total VIMTA Labs Limited, Hyderabad Water Requirement (m3/day) Existing (Before After Expansion Expansion) (3.0 MTPA) (8.5 MTPA) 525 1500 75 200 10 20 30 50 50 150 30 80 720 2000 C2-351 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.14.7 Employment Potential The mining establishment presents opportunities of employment, to various posts and under various cadre viz. management, supervisory, skilled workmen, semiskilled workmen and unskilled workmen besides casual workmen. The requirement manpower has been evaluated keeping in view the high level of mechanisation and productivity proposed for the mines on 3 shifts schedule of working for all 365 days. In order to have 7 days/week working, suitable number of relievers has been provided for the operating staff. The total manpower requirement (after expansion to 8.5-MTPA) is estimated at 290, of which 42 are executives and 248 non-executives. 2.15 Lighting and Communication 2.15.1 Mine Lighting The mine is proposed to work in 3 shifts. Depending on the nature of the working area, either shiftable or permanent lighting arrangements will be required. Lighting arrangements are proposed to be provided in the following areas: Active mining fronts - shiftable type; Dumping/backfill areas - shiftable type; Haul road/access roads-permanent type; Central Trench/Conveyor Route- shiftable or permanent lighting; and Semi-Mobile Crusher Site - shiftable or permanent lighting. Permanent illumination will be setup along the mine access roads, truck haul road, crusher, workshops, conveyor route and other permanent infrastructure. 2.15.2 Communication It is proposed to have a modern communication network at the mine-complex. The mines will be connected to the alumina refinery by a hotline telephone link. Other communication facilities may include: 2.16 Wireless communication within mines; and Satellite link communication. Sources of Pollution Virtually, all surface mining methods for any ore/mineral produce some irreversible impacts. These produce dramatic changes in the landscape due to large scale excavation. The environmental pollution due to the open cast mining, in general, could be broadly classified into the following categories: Air pollution; Despoliation of land; Solid waste/overburden; Water pollution (resources and quality); and Noise pollution and ground vibrations. VIMTA Labs Limited, Hyderabad C2-361 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution 2.16.1 Air Pollution Mining operations contribute towards air pollution in two ways: addition of gaseous pollutants to the atmosphere and the dust particles. The gaseous pollutants include NOx, SO2 and Hydrocarbons. The sources of pollutants from the existing mining activity include: Operation of Heavy Earth Moving Machinery (HEMM) which mostly run on diesel; Loading /unloading operations; Transportation of ore/overburden in dumpers; and Drilling, blasting and crushing operations. The above points can be classified as follows: Point Source/Single Source These are stationary sources, which emit air pollutants into the atmosphere from a certain fixed point. In the proposed mine, the following sources or activities form the point sources, which emit large quantities of Suspended Particulate Matter (SPM). Drilling Drilling is an important activity of mining process. It will be carried out by using Rotary blast hole drill and Jack hammers. Power drilling will be carried out with the help of compressors. This operation is one of point sources. Loading and Unloading This is another important activity in the mining operations. Loading of ore, raw materials etc, takes place through diesel driven hydraulic shovel /back-hoe. Dumpers and belt conveyors will be used for the unloading of ore, overburden etc. Crushing After the bauxite is taken out, it is subjected to crushing. This is the first step towards ore processing. This activity will be carried out in the Semi Mobile Crushing Plant unit by apron feeder. The above activities contribute to air pollution in the form of SPM. Line Sources These are normally mobile sources, which emit atmospheric pollutants in the area through which they pass. The following are the sources of air pollution falling under this category. Transportation Bauxite raised from the mine will be transported to the semi mobile crusher house using dumpers and transportation from crusher to alumina refinery will be VIMTA Labs Limited, Hyderabad C2-371 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution done through conveyor loading station. Transportation also includes movement of other vehicles in the mine lease area. The traffic on the haul roads is likely to contribute towards dust concentration in the area. However, this is more of a localized phenomenon. However, due to increased production, there will not be any addition to dust concentration in a significant manner. Dozing This activity is carried out with help of the dozers. This is other type of line source. Area Sources/Multiple Sources These constitute pollution from various sources and activities situated in the mine lease area: Overall Mining The total mine area with all its mining activities constitute the area source. These include all the mining operation activities and equipment, which contribute to atmospheric pollution from the various units/activities. Instantaneous Sources The instantaneous sources consist of air pollution due to sudden/instantaneous activities like blasting in the mine area. Blasting Blasting process involves slackening of big blocks of rocks/ore from the mines. This operation generates dust, which results in the increase of SPM concentration. It also contributes to emissions of certain gases (Oxides of Nitrogen and Ammonia) due to the use of explosives like ANFO and slurry explosives. The size of the dust particles emitted into the atmosphere plays a major role in deciding the distance to which they may be transported. Particles of larger size fall fairly rapidly and closer to their source, because of gravitational settling. However, the aerosols because of their small size may be held in suspension for years in the atmosphere and may be transported to buffer zone. Eventually, these smaller particles are collected in raindrops and fall on earth. The composition of these particles largely depends on the composition of the ore being processed. However, adequate dust suppression measures like sprinkling of water, plantation on/along the haul roads will be carried out in the mine lease. Plantation has been proved as the effective sink for air pollutants as trees are known to absorb gaseous pollutants and arrest particulate matter. Moreover, trees also act as filters for air borne particles because of their large size, high surface to volume ratio of foliage and rough surfaces of leaf and barks. VIMTA Labs Limited, Hyderabad C2-381 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution In addition, the proposed air pollution control measures (as given in Chapter-5) will contain the air pollution to a major extent during the operation of the mine. 2.16.2 Water Pollution The proposed Bauxite mine is located at hilltop. Mining is proposed to be carried out upto a maximum depth of about 20 to 30-m from surface level and ground water table (150-m below plateau top) in the area is much below the ultimate mining level. The average height of the hill from the surrounding valley is about 200-m. Therefore, ground water table is not likely to be disturbed during mining. Thus, there will not be any disturbance to groundwater resources due to the proposed mining. The wastewater generated from mines will be 200-m3/day. It is proposed to treat the wastewater in septic tanks and utilize for greenbelt development. The plateau top has no streams or nallahs, except the run-off of rainwater during monsoon. All the surface water bodies are found only in valleys and plains. Those streams are tributaries of river Indravati flowing on the western side of the deposit about 7.5-km away. Even though, the plateau top has no streams, the rainwater emerging from the top joins the streams of valleys and plains, erosion from the top may cause siltation of these streams. Sufficient measures as described in Chapter-5 will be taken to avoid erosion from the hilltop. Affect of Mine Dewatering, if any Groundwater is not encountered upto ultimate mine depth on plateau top. Hence, groundwater does not intrude into mine working. There can be only one source of water in mines, viz. rainwater. Rain water will be diverted from entering into mines through garland drains constructed ahead of mining faces. Thus, water in unpolluted state joins the natural slopes and streams. Direct precipitation of rain into mines water is very limited. However, the rainwater directly precipitated into mines will be channelised away from mine workings into sumps located intermittently. The water collected in sumps (in the mined out area) helps in recharging groundwater as most of it will percolate down the strata. The water in sumps can also be used to water the plants in backfilled area. Due to the above measures and the peripheral barrier, water from mines will not pollute the streams or springs in valleys. 2.16.3 Land Despoliation Large scale excavations are the basic causes of land despoliation. In all the surface mining methods, first the overburden has to be excavated in order to reach the ore body. Substantially, bauxite will be mined. Generally, overburden removed is much less when compared to the volume of the Bauxite ore excavated. Quantity of solid waste likely to be removed during first five years will be about 7 Mm3 (11.41 MT). However, initially, the waste will be disposed on the plateau top at a distance of about 1.0-km from active mining area. Suitably and adequate VIMTA Labs Limited, Hyderabad C2-391 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution land reclamation measures will be implemented. The overburden dumps will be protected by using parapet walls around the dumps. Garland drains also will be constructed to mitigate the damage due to land despoliation. 2.16.4 Disposal of Solid Waste Nature of Waste The solid waste likely to be generated from the mining project will be in the form of topsoil and waste rock comprising of soil, laterite, clay, lateritised Khondalite, and Khondalite. The overburden thus collected in dump yard during the initial mining period will be disposed in the mined out pits as backfill from the beginning of the fourth year. The surface area required to dump the overburden at different stages of mining is estimated based on swell factor of 20% and a dump height of 10-m. The solid waste generation details are given in Table-2.8 above. Method of Dumping Loosened rock mass obtained from blasting or ripping will be dozed, excavated and loaded into rear dumpers. The slopes of external dumps will be maintained at a maximum of 280. There will be two dumps and the total dumping area will be about 50-ha. Environmental Precautionary Measures During rain, there is a possibility of washing off of loose materials along the plateau slopes. Therefore, following precautionary measures will be undertaken for controlling the wash off. Around the dump slope, terraces are proposed; Check dams are proposed along the by boulders. During rain, water off/sediments are arrested. Settled and check dam will be cleared up by Shrubs are proposed to be planted along the terraces to prevent erosion; and Top of the dump will be properly levelled and compacted to prevent seepage of direct precipitated water. lower contours, which will be constructed passes through the dams and washsediments, in between the waste dump the help of dozer or back-hoe; 2.16.5 Noise Pollution With the introduction of the sophisticated machinery into the mining operations noise problem has become an issue. It has been established that noise interferes with speech communication, causes annoyance and distraction. The proposed mining activity envisages using heavy earth moving equipment. The anticipated noise generating equipment along with the noise levels is given in Table-2.15. VIMTA Labs Limited, Hyderabad C2-401 Rapid Environmental Impact Assessment Study for the Proposed Capacity Expansion of Bauxite Mines from 3.0 MTPA to 8.5 MTPA at Baphlimali Plateau Chapter-2 Proposed Mining and Sources of Pollution TABLE-2.15 NOISE GENERATING SOURCES Sr. No. Mining Unit Operation 1 2 3 Exploration Top-Soil (OB) Scraping Sub Soil (OB) and Bauxite Ore Loosening 4 5 Excavation and Loading Transporting 6 7 Size Reduction Water Sprinkling System Source of Noise Core Drill Dozer Operation Ripper Operation Blast Hole Drillers Blasting Shovels Operation Dumper Movement Conveyors Movement Explosive Van Service Vehicle Crushing Trucks Expected Noise Level dB(A) 95 98 90 95 90 95 90 85 75-110 75-110 110 75-110 2.16.6 Vibrations Mining activity also generates ground vibrations during the blasting. Ground vibration, fly rock, air blast, noise, dust and fumes are the deleterious effects of blasting on environment. The explosive energy sets up a seismic wave in the ground, which can cause significant damage to structures and disturbance to human occupants. It causes major damages to the pit configuration too. By adopting controlled blasting, the above said problems were greatly minimized at other existing mines. The impact is also minimized by choosing proper detonating system and optimizing total charge and charge/delay. VIMTA Labs Limited, Hyderabad C2-411