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s e l e c t i o n OF AQHS 03.05 AIR QUALITY 03.05.01 General To quantify the impact of the future mining and allied activities on the ambient air quality and to reduce the impact due to present activities, it was necessary at first. to measure the existing ambient air quality in the study area I lie background nmbionl m quality (AAQ) in respect of suspended particulate matter (SPM), sulphur dioxide (SO:-?), oxides of Nitrogen (NOx), carbon monoxide (CO) and dustfall has been determined quantitatively through a planned field monitoring. 03.05.02 Monitoring Stations To determine the ambient air quality monitoring stations were set up at seven location-; (one station at OMC COB plant was shifted to village Patna in 2nd season) Out of the seven locations one station was set up in the core zone. The details pertaining to their locations nr« given in Table No. 03.04. The AAQ station locations are shown in Drawing No MEC/1 I/S2 7443/15. While deciding the locations of the AAQ monitoring stations views of the Departm-'n' of Environment (DOEn), Ministry of Environment and Forests, were considered Following points were also considered, while fixing ttie number and location ol AAQ monitoring stations. As a result of mining, ambient air quality is affected mostly due to plying of dumpers and also due to other operations like drilling, blasting and overburden dumping Ambient air quality is expected to be affected in an area in and around the mines Keeping this in view, it was decided to monitor mainly the core and nearby bufte r zones. While fixing the number of AAQ monitoring stations, the model of United States Environmental Protection Agency (USEPA, 1975b) was utilised The model !•; presented in Table No. 03.05. The model suggests that minimum number of AAO stations should be four. However, as mentioned earlier, more stations were set u; A model suggested by Houghland and Stephens. (Ref. "The Design of Air Qualit. monitoring Network," R E. Munn, 1981) has been utilised to lix up the location o monitoring stations. This model suggests setting up of monitoring stations at thos lo cat ions where the probability of occurrence of maximum ground level co ncentr a ti - >•• (GLC) is high. The probability factor was found by determining the coverage lack MiSHIlAL MINES PV T LTD ().i-()(>

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s e l e c t i o n O F A Q H S

0 3 . 0 5 AIR Q U A L I T Y

0 3 . 0 5 . 0 1 G e n e r a l

To q u a n t i f y the impac t o f the fu tu re m i n i n g a n d a l l i ed ac t i v i t ies on the a m b i e n t air qua l i t y a n d to r e d u c e the impac t d u e to p r e s e n t ac t i v i t i es , i t was n e c e s s a r y a t f i r s t . to m e a s u r e the ex i s t i ng a m b i e n t air qua l i t y in the s tudy a rea I l ie b a c k g r o u n d n m b i o n l m q u a l i t y ( A A Q ) in r e s p e c t o f s u s p e n d e d p a r t i c u l a t e mat te r ( S P M ) , su lphu r d i ox i de (SO:-?), o x i d e s o f N i t r o g e n ( N O x ) , c a r b o n m o n o x i d e ( C O ) a n d d u s t f a l l h a s b e e n d e t e r m i n e d q u a n t i t a t i v e l y t h r o u g h a p l a n n e d f ie ld m o n i t o r i n g .

0 3 . 0 5 . 0 2 M o n i t o r i n g S t a t i o n s

To d e t e r m i n e the a m b i e n t a i r qua l i t y m o n i t o r i n g s ta t i ons we re set up a t s e v e n loca t ion- ; ( one s t a t i o n a t O M C C O B p lan t w a s s h i f t e d to v i l l age Pa tna in 2 n d s e a s o n ) Out o f the s e v e n l o c a t i o n s o n e s ta t i on was set up in the co re z o n e . T h e de ta i l s p e r t a i n i n g to the i r l o c a t i o n s n r« g i v e n i n T a b l e No. 03 .04 . T h e A A Q s t a t i o n l oca t i ons are s h o w n i n D r a w i n g No M E C / 1 I / S 2 7 4 4 3 / 1 5 .

W h i l e d e c i d i n g the l oca t i ons o f the A A Q m o n i t o r i n g s ta t i ons v i e w s o f the D e p a r t m - ' n ' o f E n v i r o n m e n t ( D O E n ) , M in i s t r y o f E n v i r o n m e n t a n d F o r e s t s , w e r e c o n s i d e r e d

F o l l o w i n g po in t s w e r e a l so c o n s i d e r e d , wh i le f i x ing t t ie n u m b e r a n d l o c a t i o n o l A A Q m o n i t o r i n g s t a t i o n s .

• As a resu l t of m in i ng , a m b i e n t a i r qua l i t y is a f f e c t e d mos t l y d u e to p l y i n g of d u m p e r s a n d a lso d u e t o o the r o p e r a t i o n s l ike d r i l l i ng , b l a s t i n g a n d o v e r b u r d e n d u m p i n g

• A m b i e n t air qua l i t y is e x p e c t e d to be a f f e c t e d in an a r e a in a n d a r o u n d the m i n e s K e e p i n g th is i n v i e w , i t w a s d e c i d e d to m o n i t o r ma in l y the c o r e a n d n e a r b y b u f t e r

z o n e s .

W h i l e f i x i n g the n u m b e r o f A A Q m o n i t o r i n g s ta t i ons , the m o d e l o f U n i t e d S t a t e s E n v i r o n m e n t a l P r o t e c t i o n A g e n c y ( U S E P A , 1975b) was u t i l i s e d The m o d e l !•; p r e s e n t e d i n T a b l e No . 0 3 . 0 5 . T h e m o d e l s u g g e s t s that m i n i m u m n u m b e r o f A A O s t a t i o n s s h o u l d be four . H o w e v e r , as m e n t i o n e d ea r l i e r , m o r e s ta t i ons w e r e set u ;

• A m o d e l s u g g e s t e d by H o u g h l a n d a n d S t e p h e n s . (Re f . " T h e D e s i g n o f Air Q u a l i t . m o n i t o r i n g N e t w o r k , " R E. M u n n , 1981) h a s b e e n u t i l i sed to l ix up the l o c a t i o n o m o n i t o r i n g s t a t i o n s . Th is m o d e l s u g g e s t s se t t i ng up o f m o n i t o r i n g s t a t i o n s a t t h o s lo cat ions w h e r e the p r o b a b i l i t y of o c c u r r e n c e of m a x i m u m g r o u n d l eve l co n c e n t r a t i - >•• ( G L C ) i s h i gh . The p r o b a b i l i t y f ac to r w a s f o u n d by d e t e r m i n i n g the c o v e r a g e l a c k

MiSHI lAL MINES PV T LTD

().i-()(>

(A | k)" for r e s i d e n t i a l l o c a t i o n s a r o u n d t h e m i n e s w h i c h a re l i ab lo to bo n l f o c t o d t>y th« po l l u tan ts . C o v e r a g e f a c t o r s "A ' fo r a l l t he p o t e n t i a l l o c a t i o n s w e r e c a l c u l a t e d by th« following f o r m u l a :

F R E Q ( k ) = ( 1 + ^ )

W h e r e

C o v e r a g e f a c t o r o f the m o n i t o r i n g s i te i n the k,h d o w n w i n d s e c t o r f r o m s o u r c e .

F R E Q ( k ) = F r e q u e n c y o f w i n d d i r e c t i o n in the k th s e c t o r

D. = D i s t a n c e f r o m the s i te to the s o u r c e .

S E L E C T E D A A Q MONITORING STAT IONS

Table. 03.04

SL. No.

Name of stat ion D is tance/D i rec t ion ( f rom quarry)

' C o v e r a g e Fac to r A = F R E Q ( k ) / d ' + D,)

S ta t i on s ta tus .

1. Roof of Saruabi l Mine Office (A,)

1 50 m f rom nearest sou rce /NE

7 21 C o r e zone

2. Kaliapani Central Townsh ip Roof of Qr. No. 0 - 1 4 (A2)

4.25 Km/W 1 58 Bu f fe r zone (Met stn )

3. COB Plant of OMC. roof top of COB plant weigh bridge. (A , , ) (24 samples in 1 st season & 9 samples in 2nd season)

2 . 2 5 K m / W S W 2.55 Bu f fe r zone

4. Village Patna,erected plat form near schoo l (A 3 J ) (15 samples in 2nd season and 24 samples each in 3rd & 4th seasons ) .

5.5 Km/WNW 1.07 Buf fer zone (cont ro l stn )

5. Kamarda Resident ia l township (AJ

0 .75Km/ENE 5.14 Bu f fe r zone

6. Sukurangi Camp (A5) 1.0 Km/SW 4.15 Bu f fe r zone

7. Village Kansa, roof top of forest guard 's quarter. (A ()

3 .75Km/ENE 1.89 Bu f fe r zone

As per H o u g h l a n d a n d S t e p h e n m o d e l for f ix ing the loca t ion of Air qua l i t y m o m t o n m s s ta t ions (Ref : The d e s i g n o f air qua l i t y mon i t o r i ng ne two rk ; R . E . M u n n , 1981)

Basic -.vmdrose at S u k u r a n g i v i l l age was used for ca l cu la t i on of c o v e r a g e fac to r Win-ir-_-of Suku rang i v i l l age w a s s u p p l i e d by D i reco ra te of M in i ng a n d G e o l o g y : Gov t of O r i s - ; •)

MISF1ILAL MINES PVT. LTD

03-07

T a b l e 03.05

R E G U L A T O R Y M I N I M U M N U M B E R O F M O N I T O R I N G SITES ( E P A , 1 9 7 5 b )

C lass i f i ca -t ion of reg ion

Pol lu tant Reg ion popu la t i on M i n i m u m n u m b e r of air qua l i ty mon i t o r i ng s i tes

I S u s p e n d e d par t i cu la tes h i -vo l

Less than 100000 1 0 0 0 0 0 - 1 0 0 0 0 0 0 1 0 0 0 0 0 0 - 5 0 0 0 0 0 0

4 4 + 0 6 per 100000 popu la t ion 7 .5+0 .25 per 100000 popu la t ion

Tape sample r A b o v e 5 0 0 0 0 0 0 1 2 * 0 . 1 6 per I 0 0 0 0 0 popu la t i on One per 2 5 0 0 0 0 popu la t i on upto e ight s i tes

Su lphur d iox ide bubb le r

Con t i nuous

Less than 100000 1 0 0 0 0 0 - 1 0 0 0 0 0 0 1 0 0 0 0 0 0 - 5 0 0 0 0 0 0 Above 5 0 0 0 0 0 0 Less than 100000 1 0 0 0 0 0 - 5 0 0 0 0 0 0 Above 5 0 0 0 0 0 0

3 2.5 + 0.5 per 100000 p o p u l a t i o n 6+0 .15 per 100000 popu la t i on 6+0 .05 per 100000 p o p u l a t i o n 1 1+0.15 per 100000 popu la t i on 6 t-0.05 per 100000 p o p u l a t i o n

Ca rbon monox ide

Less than 100000 1 0 0 0 0 0 - 5 0 0 0 0 0 0 Above 5 0 0 0 0 0 0

1 1+0.15 per 100000 popu la t i on 6+0 05 per 100000 popu la t i on

P h o t o c h e m i c a l ox idan ts

Lass than 100000 1 0 0 0 0 0 - 5 0 0 0 0 0 0 Above 5 0 0 0 0 0 0

1 1+0.15 per 100000 popu la t i on 6+0 .05 per 100000 popu la t i on

N i t rogen d iox ide con t inuous bubb ler

Less than 100000 1 0 0 0 0 0 - 1 0 0 0 0 0 0 Above 5 0 0 0 0 0 0

3 4 + 0.6 per 100000 popu la t i on 10

I I S u s p e n d e d par t i cu la tes

3 h i -vo ls 1 tape samp lo r

Su lphur d iox ide

3 bubb le r 1 c o n t i n u o u s

III S u s p e n d e d par t i cu la tes Sulphur d iox ide Ni t rogen d iox ide

1 h i -vo l

1 bubb le r 2 bubb le r s

— MISRILAL MINES PVT. LTD

03-08

V .

For e a c h s t a t i o n ' A w a s c a l c u l n l o d . T h o s t n l i o n s w h i c h q n v n h i g l m r ' A ( ' v a l u n s w.>m' t a k e n as m o n i t o r i n g s t a t i o n s . The a v e r a g e w i n d r o s o d i a g r a m a t S u k u r a n g i , a t a d i s t a n c e o f a b o u t 1.0 k m , f r om the m i n e s in SW d i r e c t i o n w a s u s e d for c a l c u l a t i o n o l F R E Q ( k ) . T h e b a s i c w i n d rose d i a g r a m (at S u k u r a n g i v i l l age ) w a s p r o v i d e d b y tho D i r e c t o r a t e of M i n i n g a n d G e o l o g y , Gov t , o f O r i s s a C o v e r a g e fac to r A ' for the

- - s t a t i o n s h a v e b e e n g i v e n in T a b l e No . 03 .04 . Ou t o f t he p o t e n t i a l m o n i t o r i n g s t a t i o n s b u f f e r z o n e l o c a t i o n s h a v i n g c o m p a r a t i v e l y h i g h e r co v e r a go fac to r (1 58 to / ? t ) s e l e c t e d as m o n i t o r i n g s ta t i ons . The c o n t r o l s ta t i on w a s set up in v i l l age P a t n a (A ) at a l ong d i s t a n c o (5 .5 k m ) f rom p ro jec t in a d i r o o t i o n w h o m w i n d Ir«»i)«ii»nr-.if>nn- I " . A l s o , in the S u m m e r s e a s o n w h e n the w i n d s p e e d is h i g h in th is r e g i o n this s ta t i on (A ) c o u l d g i ve an i dea w e a t h e r the p o l l u t a n t s are d i s p e r s e d t o s u c h l o n g d i s t a n c e s . D u e t o p r e s e n c e o f t w o s t a t i o n s in W - S W - W S W s e c t o r a t v a r i o u s d i s t a n c e s (A s a t 1.0 km a n d A? a t 4 .25 k m ) the t h i r d s ta t i on A3 t w a s s h i f t e d to v i l l a g e P a t n a (A3 2 ) in the s e c o n d s e a s o n t o s e r v e a s c o n t r o l s ta t i on .

• D u e to the h i l l s on the N o r t h e r n a n d S o u t h e r n par t o f the l e a s e a r e a w i n d f r e q u e n c i e s f r o m / t o w a r d s t h e s e d i r e c t i o n s are less a n d a l so t h e r e i s no h u m a n h a b i t a t i o n over t h e s e r e g i o n s . K e e p i n g th is i n v i e w , no A A Q m o n i t o r i n g s t a t i o n w a s set up on N o r t h e r n a n d S o u t h e r n h i l l y t e r r a i n .

0 3 . 0 5 . 0 3

M o n i t o r i n g s c h e d u l e

As m e n t i o n e d e a r l i e r i n C h a p t e r 01 m o n i t o r i n g w a s c a r r i e d out i n W i n t e r ( 2 1 0 1 . 9 0 to 3 0 . 0 3 . 9 0 ) , S u m m e r ( 1 0 . 5 . 9 0 t o 1 0 . 0 7 . 9 0 ) , M o n s o o n ( 2 3 . 0 7 . 9 0 t o 2 2 . 0 9 90) a n d Post m o n s o o n ( 2 4 . 1 0 . 9 0 t o 2 2 . 1 2 . 9 0 ) s e a s o n s . I n e a c h s e a s o n a t e a c h s t a t i o n m o n i t o r i n g w a s p l a n n e d to be d o n e fo r o n e m o n t h (4 w e e k s ) , tw i ce a w e e k , tor 24 h o u r s . 3 e igh t h o u r l y s a m p l e s w e r e t a k e n . B e t w e e n two m o n i t o r i n g m o n t h s a g a p o f - 1 - 2 m o n t h s w a s p l a n n e d E n v i r o n m e n t a l M o n i t o r i n g d a t a o f 1994 is e n c l o s e d as a d d e n d u m r e p o r t in v o l u m e - l l o f th is r epo r t .

0 3 . 0 5 . 0 4

S a m p l i n g a n d A n a l y s i s p r o c e d u r e

A A Q m o n i t o r i n g w a s d o n e us ing h i g h v o l u m e air s a m p l e r s . S P M w a s c o l l e c t e d o n g l a s s m i c r o f ib re f i l ter p a p e r s . G a s e o u s p o l l u t a n t s ( S O j . N O J w e r e c o l l e c t e d b y i rnp inger b u b b l i n g m e t h o d a n d a n a l y s e d c o l o r i m e t r i c a l l y a s per s t a n d a r d m e t h o d s . C O w a s m o n i t o r e d u s i n g MSA d e t e c t o r t u b e s .

0 3 . 0 5 . 0 5 R e s u l t s a n d D i s c u s s i o n s

F r o m the m o n i t o r e d da ta the s u m m a r i s e d A A Q resu l t s for the s e v e n l o c a t i o n s are p r e s e n t e d a n d g i ven i n T a b l e N o . 03 .06 . G r a p h i c a l p r e s e n t a t i o n o f the S P M v a l u e s ( M a * . Min . a n d Avg ) h a v e b e e n s h o w n i n F i g . 0 3 . 0 5 .

C o m p a r i s o n o f the c o n c e n t r a t i o n v a l u e s o l SPM. SO . N O a n d CO w i th the ind ' i s t r i i l a n d ~ t e d use s t a n d a r d s la id d o w n by C e n t r a l Po l l u t i on C o n t r o l R. , u d ( C I ' C B i .!•,.>.•. . >h.it a ' a l l ' h e s ta t i ons , in al l the s e a s o n s (1 0 0 % t imes) the SPM. SO. . N ( . \ a n d CO i . mom m m - n . a ues are we l l w i t h i n the p r e s c r i b e d u p p e r l imi ts la id d o w n by C P O B

V — MISHILAL MINES PV f L I U -

03-09