Pollution bar and control schemes continue to germinate in response to increased consciousness and altering environmental ordinances. The Pollution Prevention ( P2 ) scheme is having important attending in industries all over the universe, over end-of-pipe pollution control and direction scheme. The bing P2 models are reviewed and compared to place restrictions of these models. We have proposed a Pollution Prevention ( P2 ) and Pollution Control ( Personal computer ) model to get the better of the restriction of bing models. Two of import scenarios, design stage and retrofitting of bing workss are considered in proposed model.

Attempts in air pollution control are focused on either development of advanced engineerings to cut down the emanations or use of bing engineerings in optimum mode. World Bank group study ( 1998 ) pointed out that pollution control shall see both particulate every bit good as gaseous pollutants. Mcilvaine, B ( 2006 ) noted that techno-commercial rating of the engineerings to confront the future challenges of stringent norms is necessary. It is noted that efficiency of every air pollution control device depends on pollutant features. The air pollutant features non merely act upon the public presentation of control equipments but besides influence wellness jeopardies. In this regard Government of India revised National Ambient Air Quality Standards ordering upper bounds for PM2.5 and PM10 ( NAAQM Notification GOI 2009 ) .

Quantification of environmental and societal cost due to emanations is a major challenge. However, in the recent yesteryear some attending is paid to gauge the wellness cost and quantify the same. These appraisal methods are loosely based on a ) response maps and intensifying factors b ) affect of ague or chronic exposure to the pollutants and degree Celsius ) dose response surveies. Akbar et Al. ( 2003 ) proposed a method that buttocks and value the inauspicious wellness impacts due to exposure to air pollutants. Friedrich et Al. ( 2001 ) presented a methodological analysis of medical costing, it involve dispersion surveies of the air pollutants right from the beginning boulder clay its concluding impact.

Choice of best possible P2 and Personal computer scheme needs a basically sound numerical/ analytical technique. Optimization is a major enabling country in this respect which evolved from a methodological analysis of academic involvement into a engineering that has continues to do a important impact. Shaban et Al. ( 1997 ) proposed an optimisation theoretical account for choice of suited control option to minimise pollution burden and maximise the net incomes. Multi Objective Optimization ( MOO ) has found extended usage in work outing the P2 and PC jobs in procedure industries ( Mavrotas, 2006 ; Martinez et Al. 2010 ) . However, the optimisation theoretical accounts reported in literature do non see wellness cost of air pollutants entirely in the nonsubjective maps for choice of optimum control scheme.

With above preamble, the wide research aim of the present survey is to explicate a mathematical theoretical account which minimizes the combined environmental and economical cost through optimum choice of air pollution bar and control scheme within the frame work of statutory demands. To accomplish the wide aims presented above the specific research aims of the work identified are as follows:

To develop a generic mathematical theoretical account for optimum choice of air pollution bar & A ; control schemes after sing both economical and environmental cost.

To measure the efficaciousness of the proposed theoretical account for optimum choice of air pollution control strategies sing multiple beginnings, multiple air pollutants and multiple air pollution control devices at the same time. Besides to research the benefits of resource recovery and reuse while placing optimum scheme.

Integrating the consequence of pollutant ‘s features on the efficiency of control equipment while placing the optimum air pollution control scheme utilizing the proposed mathematical theoretical account.

Confirmation of proposed theoretical account for designation of environmental friendly natural stuff and techno-commercial rating of the same for decrease of air pollutants at beginning.

Application of the theoretical account to propose necessary alterations in the bing air pollution control system to accomplish norms prescribed by regulator in commercially runing procedure workss.

A mathematical/optimization theoretical account for choice of optimum air pollution bar and control scheme is developed. The aim of the theoretical account is to minimise combined economic and environment cost. The theoretical account considers that multiple air pollutants ( P ) are breathing from multiple air emanation beginnings ( I ) and multiple control options ( J ) are available for application.

The cost incurred during the operation of the air pollution preventative steps ( ) and control ( ) is considered. Such cost besides includes power ingestion, care cost, labour cost, public-service corporation cost and others.

Operating cost = ( 1 )

In the above equation cyberspace present value is calculated by taking combination of local involvement rate and expected rate of rising prices i.e. icom. In above equations ( 1 ) a binary variable is considered. If an option is non selected for application over any peculiar beginning so and becomes 1 when option is selected.

Similarly, the cost incurred during hard-on and commissioning of the air pollution bar step ( ) and control ( ) equipments is considered as installing cost. It is good known that cost of the equipment depends on the capacity, stuff of building and handiness of the equipment.

Installation cost = ( 2 )

Quantification of wellness impact for air pollutants is considered utilizing the impact tract analysis methodological analysis ( Friedrich et al. 2001 ) . Friedrich et Al. ( 2001 ) has calculated the value of a ‘year of life lost ‘ ( YOLL ) due to air pollution by sing value of statistical life ‘ ( VSL ) . It is so calculated for net present value of a series of discounted one-year values. The ratio of VSL and value of a YOLL therefore obtained depends on the price reduction rate. Besides Nonfatal and fatal malignant neoplastic diseases ( depending on the YOLL for each malignant neoplastic disease type ) has been considered. The wellness cost associated with emanation of classical pollutant P is.The pollutants are emitted into the ambiance through beginning I with mercantile establishment concentration and flow rate Qi. The footings indicate the entire length of the operation.

Health cost = ( 3 )

Some of the pollution control equipment recovers utile resources. The benefit associated with such recovery is besides considered while choosing the optimum scheme. In the present survey, a generic map RMC is proposed which relates benefits of recovery. Here, RMC can be visualized as a changeless that gives cost in US dollars per unit measure of stuff recovered

Cost of stuff recovered= ( 4 )

Objective map Z is to minimise the sum cost which includes operating, installing and wellness cost.

( 5 )

The theoretical account is generic plenty for application to propose optimum P2 and PC schemes. It can be extended farther by integrating the cultural and societal cost, provided these costs can be estimated in due class. The consequence of pollutant feature on efficiencies of the control equipment and their optimum choice are besides possible utilizing presented theoretical account. The benefits associated with recovery of resources are considered while choosing optimum air pollution control scheme.

The efficaciousness of the proposed optimisation theoretical account is demonstrated for choice of optimum air pollution control scheme. The choice of optimum air pollution control scheme is illustrated by sing simulation instance surveies of a typical cement works and a thermic power works. The existent information is collected from four commercially operated cement workss located in province of Gujarat for three seasons in a twelvemonth for four old ages. Three pollution control devices viz. bag filter, electrostatic precipitator and cyclone centrifuge were considered. The MINLP job is solved utilizing commercial package GAMS. The consequence of regulative norms on the optimum choice of the air pollution control devices are summarized in Table No. 1.

Table No. 1: Consequence of mercantile establishment emanation norms on optimum choice of air pollution control equipment for cement works.

Crusher

65

40

40

1

1

1

Raw factory

65

40

40

1

1

1

Coal factory

65

40

40

1

1

1

Cooler

65

40

40

1

1

1

Cement Factory

65

40

40

1

1

1

Crusher

110

49

49

1

1

Ten

Raw factory

110

49

49

1

1

Ten

Coal factory

110

49

49

1

1

Ten

Cooler

110

49

49

1

1

Ten

Cement Factory

110

49

49

1

1

1

Crusher

250

74

74

1

1

Ten

Raw factory

250

74

74

1

1

Ten

Coal factory

250

74

74

Ten

1

1

Cooler

250

74

74

Ten

1

1

Cement Factory

250

74

74

1

1

Ten

Crusher

275

77

77

1

1

Ten

Raw factory

275

77

77

Ten

1

1

Coal factory

275

77

77

Ten

1

1

Cooler

275

77

77

Ten

1

1

Cement Factory

275

77

77

Ten

1

Ten

Crusher

300

80

80

Ten

1

1

Raw factory

300

80

80

Ten

1

1

Coal factory

300

80

80

Ten

1

1

Cooler

300

80

80

Ten

1

1

Cement Factory

300

80

80

Ten

1

Ten

It can be noted from Table 1 that as mercantile establishment emanation norms become rigorous all the control equipments are used to cut down emanations to needed degrees. During rigorous norms wellness cost is least as illustrated in Fig.1 ( a ) . However, installing and operating cost are higher during rigorous norms and lessenings as mercantile establishment norms relaxed, this can be observed from Fig 1 ( a ) & A ; Fig.1 ( B ) . The benefit of retrieving resources and entire cost is illustrated Fig. 1 ( B ) . The net income obtained by retrieving stuff is about 40 times more than cumulative cost incurred by installing, operation of air pollution control equipments and wellness cost for the instance under consideration. Similarly, a typical power works is taken into consideration for application of proposed theoretical account. Actual information of two commercially operated thermic power workss is collected thrice a twelvemonth for two old ages. Electrostatic precipitator, bag filter and cyclone centrifuge are considered for this instance. The consequence of mercantile establishment emanation norms on economic every bit good as wellness cost for power works is illustrated in Figure 2 ( a, B ) . From the survey it can be noted that 400 mg/m3 of PM is found to be optimum emanation norms for power works. Hence, the efficaciousness of the proposed theoretical account has been satisfactorily evaluated by sing simulation instance surveies of a typically operated cement works and a thermic power works.

Variation in the installing and wellness cost.

Variation in the operating cost

Figure 2: Consequence of mercantile establishment emanation norms on economic and environmental cost for cement works

a. Consequence of mercantile establishment emanation norms on Operating, installing and wellness cost for thermic power works.

B. Consequence of mercantile establishment emanation norms on Entire cost for thermic power works.

Figure 2: Consequence of mercantile establishment emanation norms on economic and environmental cost for power works

The commercial procedure packages Aspen plusA® and CAMCADA® are used for simulation of air pollution control devices. The simulations are carried out to measure dependence of aggregation efficiencies of control devices on atom features. Particle removal efficiency of control equipment when operated entirely every bit good as when they are operated in combination with other control equipments are presented in Fig. 3 ( a ) & A ; Fig. 3 ( B ) severally.

Collection Efficiency individual pollution control devices

Collection Efficiency of control devices in series.

Figure 3: Collection efficiencies of air pollution control devices with regard to particle size.

These simulation consequences along with economic and environmental cost are considered for optimum choice of air pollution control scheme. The proposed optimisation theoretical account is used to minimise entire cost consisting of economic cost & A ; wellness cost due to emanation of particulate affair including ultrafine particulate affair ( PM2.5 & A ; PM10 ) . The simulation consequences are depicted in Table 2.

Table No.2: Consequence of mercantile establishment emanation norms sing ultrafine on optimum choice of air pollution control devices.

10

15

25

30

30

Incinerator

1

1

1

1

1

1

Desiccant

1

1

1

1

1

1

Boiler

1

1

1

1

1

1

15

20

30

35

35

Incinerator

1

1

1

1

1

1

Desiccant

1

Ten

1

1

1

1

Boiler

1

1

1

1

1

1

20

25

35

40

40

Incinerator

1

1

1

1

Ten

1

Desiccant

1

1

1

1

Ten

1

Boiler

Ten

1

1

1

1

1

30

35

45

50

50

Incinerator

1

1

1

1

Ten

1

Desiccant

1

1

1

1

Ten

1

Boiler

1

1

1

1

Ten

1

35

40

50

55

55

Incinerator

1

1

1

Ten

Ten

1

Desiccant

1

1

1

Ten

Ten

1

Boiler

1

1

1

1

Ten

1

45

50

60

70

70

Incinerator

1

1

1

Ten

Ten

1

Desiccant

1

Ten

1

Ten

Ten

1

Boiler

1

1

1

Ten

Ten

1

50

55

65

80

80

Incinerator

1

1

Ten

Ten

Ten

1

Desiccant

1

1

Ten

Ten

Ten

1

Boiler

1

1

1

Ten

Ten

1

It is noted from Fig. 4 ( a ) & A ; Fig. 4 ( B ) that economic cost and wellness cost are comparatively higher for respirable particulate affair. Similarly entire cost is besides comparatively higher when respirable particulate affair is present as illustrated in Fig.4 ( degree Celsius ) . This is due to choice of costlier air pollution control devices to capture all right atoms to order degree as depicted in Table 2. From the Fig.4 ( degree Celsius ) it can be noted that 150 mg/m3 is found to be optimum emanation norms.

Consequence of mercantile establishment emanation on economic cost.

Consequence of mercantile establishment norms on environmental cost.

Consequence of mercantile establishment norms on Entire cost

Figure 4. Consequence of mercantile establishment emanation norms on economic cost and wellness cost of particulate affair

Emission norms are expected to go rigorous as clip progresses. The bing P2 models are reviewed and compared to place their drawbacks. We have proposed a P2 and PC model by integrating the restrictions of bing models. Application of the proposed mathematical theoretical account is explained for optimum choice of P2 and PC options within the proposed model. The theoretical account can be used to measure the techno-commercial feasibleness of choosing the alternate natural stuff. The instance survey of the typical public-service corporation subdivision or commercially operated procedure workss are studied for choice of optimum fuels. The cost of steam coevals utilizing assorted fuel every bit good as cost of air pollution control scheme along with wellness cost is considered. The existent information from industrial boilers operated with assortment of fuels is collected from manufacturer/suppliers of commercial boilers. The non handiness of the natural gas at distant locations is besides considered while measuring the options. The simulation consequences are tabulated in Table 3 & A ; 4.

Table 3: Optimum choice of P2 and PC scheme for fixed operating old ages.

25

25

25

1

Ten

Ten

1

Ten

1

Ten

Ten

40

28

28

1

Ten

Ten

1

Ten

1

Ten

Ten

160

54

54

Ten

1

Ten

1

Ten

1

Ten

Ten

175

58

58

Ten

1

Ten

1

Ten

1

Ten

Ten

190

62

62

Ten

Ten

1

1

Ten

1

Ten

Ten

205

65

65

Ten

Ten

1

1

Ten

1

Ten

Ten

220

68

68

Ten

Ten

1

1

Ten

1

Ten

Ten

235

72

72

Ten

Ten

1

1

Ten

1

Ten

Ten

250

75

75

Ten

Ten

1

1

Ten

1

Ten

Ten

Table 4: Optimum Selection of P2 and PC scheme for alteration in operating old ages.

3

Ten

Ten

1

1

1

Ten

Ten

Ten

4

Ten

Ten

1

1

1

Ten

Ten

Ten

5

Ten

Ten

1

1

Ten

1

Ten

Ten

6

Ten

Ten

1

1

Ten

1

Ten

Ten

7

Ten

Ten

1

1

Ten

1

Ten

Ten

8

Ten

Ten

1

1

Ten

1

Ten

Ten

9

Ten

Ten

1

1

Ten

1

Ten

Ten

10

Ten

Ten

1

1

Ten

1

Ten

Ten

BH=bag house, HEC= high efficiency cyclone, CS=caustic scrubber

Hence, the efficaciousness of the theoretical account to choose optimum preventative steps along with control scheme is demonstrated. Natural gas has been selected as a best environmental friendly fuel for the long term operations. However, for the short term operations coal has been selected.

The province of Gujarat is a major hub/contributor for the production of dye and dye-intermediate industries. The industrial estate of Ahemdabad territory part is holding more than 500 little, medium and big graduated tables of dye and dye intermediate industries. Most of these are in operation since last three decennaries. Scope of the survey is limited to rating of APMS and to propose suited extra extenuation steps required to do the APMS adequate. The theoretical account proposed in this survey is used to choose the optimum air pollution control scheme to run into the particulate emanation norms of 150 mg/m3. More than 75 dye units which utilize spray desiccants responsible for particulate affair emanations are monitored. The elaborate design specifications of APCM are collected for such units. Actual sampling/monitoring and analysis of the procedure works is carried out utilizing standard methods. Industrial units with unequal APMS are identified.. The commercial cost for alteration of bing control devices every bit good as for extra control step are obtained from the manufacturers/suppliers of these equipments. The proposed optimisation theoretical account is applied to propose an optimum air pollution control scheme for each industry. The simulation consequences are presented in Table 5. From the Table 5 it can be noted that it is possible to accomplish the mercantile establishment emanation norms by retrofitting bing APMS. The alterations of Venturi are suggested for all the units considered. However, cyclone alterations are suggested to five out of seven units.

Table 5: An optimum Choice of air pollution control scheme for standard mercantile establishment emanation norms for particulate affair ( 150 mg/Nm3 ) .

1.

Nichem industries

8.8

1.1

1.3294

11.229

Ten

Ten

1

1

2.

Multi colourchem

8.8

1.1

2.1714

21.971

Ten

Ten

1

1

3.

Appollo

8.8

1.1

1.7726

11.672

Ten

Ten

1

1

4.

Shivanand polymer

8.8

0.6

1.1522

10.552

1

Ten

Ten

1

5.

Dynamic Dyes ltd.

8.8

1.1

1.5954

11.495

Ten

Ten

1

1

6.

Alfa

8.8

1.1

1.5954

11.495

Ten

Ten

1

1

7.

MAC

8.8

0.6

0.9306

10.330

1

Ten

Ten

1

An optimisation theoretical account is developed for optimum choice of air pollution bar & A ; control schemes after sing both economical and environmental cost. The environmental cost in footings of wellness consequence due to emanation of assorted air pollutants into ambiance is entirely considered while optimising entire cost

The efficaciousness of the theoretical account is demonstrated for multiple air pollutants, multiple beginnings and multiple control equipment. Benefits due to resource recovery is besides been explored utilizing same theoretical account.

The air pollution control equipments are simulated by commercial simulators to measure the consequence of PSD on their aggregation efficiencies. The efficaciousness of proposed mathematical theoretical account is demonstrated with the aid of a typical pharmaceutical works.

A new P2 and PC model is proposed which overcome the limitations/drawbacks of the bing models reported in unfastened literature. Two of import scenarios, design stage and retrofitting of bing workss are considered in proposed model. Use of the proposed mathematical theoretical account is explained for optimum choice of P2 and PC options within the proposed model. A instance survey is presented for public-service corporation subdivision sing assortment of fuel and control techniques.

The theoretical account has been used to propose necessary alterations for equal APMS in the commercial procedure industries to accomplish the regulative norms.