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Result and Discussion



3.2      Result and Discussion

The classified image of Nagpur district is shown in Fig. 4. Agricultural area in each Talukadigitized as polygon cover and slope direction is shown in Fig. 5.


Figure 4: Classified Image of Nagpur District


FFigure 5: Slope Direction Map with Agriculture and Water- bodies



The estimated runoff from the cultivated land of various tehsils in Kharifand rabiseason is presented in Tables 8 and shown in Fig 6. It is observed that total runoff from cultivated land is the maximum in Narkher and minimum in Ramtek tehsil of Nagpur district.


Figure 6: Estimated runoff from the cultivated land of various tehsils


The amount of pollutant generated in agricultural land use of a tehsil unit is the function of different cropping pattern, rainfall variation, fertilizer applied and area under cultivation. Considering the amount of fertilizer applied and fertilizer requirement by different types of crops, the amount of fertilizer used was estimated. The corresponding remaining fertilizer i.e. the excess nutrient load which remains in the soil after Kharifand Rabiseason from each Talukais presented in Tables 9 and 10.

This amount of load generated from each Talukawas classified in different ranges and mapped onto the base map for Kharifand Rabiseason as shown in Figure 7 and 8, respectively. It is seen that most of the Talukas generate nutrient load in the range 2051450 kg To 4081517 Kg per year. The highest load is generated from the agricultural land in Narkher Taluka.


Figure 7: Total nutrient load generated in Kharif season



Figure 8: Total nutrient load generated in Rabiseason


The unused fertilizer is carried with overland flow after the rainfall, which either meets the nearby water body or spreads over the land. The direction of runoff flow from agricultural land is also shown in Figure 5. It is observed that agricultural areas in Narkher, Katol, Bhiwapur and Umrer Talukas do not contribute to water pollution, whereas the areas near Major River Kanhan severely contribute to surface water pollution. This is shown in Figure 9 by creating a buffer zone of 2 km radius around each water body in GIS and mapping slope direction on it. Direction of slope indicates the sensitivity of water body to receive agricultural pollution from adjacent area. It is observed that the water bodies in Narkher, Kuhi and Maunda Taluka, which generates highest pollution load, would receive maximum nutrient loading from agricultural runoff and maximum nutrient loading from agricultural runoff in Narkher goes into the Vardha catchments.


Figure 9: Buffer- zone Map with 2Km distance around water bodies in Nagpur District


The simulated pollutographs i.e. the graphs showing pollutant load carried with runoff after Kharifand Rabiseason in three major talukas which generate maximum agricultural pollution load are presented in Figs 10 to 12. (i.e. pollutograph for TN ad TP.) Since, the fertilizers are again applied in the same proportion at the start of each Kharifand Rabiseason, there is accumulation of nutrient in the soil. The accumulated load is considered for simulation of pollutographs for the next cycle of Kharifand Rabiseason and are termed as projected scenarios. The projected pollutographs for subsequent Kharifand Rabiseason in talukas with highest nutrient loading are also presented in Figures 10 to 12.


Figure 10: Nitrogen and Phosphorus Load in the Runoff from Narkher Taluka



Figure 11: Nitrogen and Phosphorus Load in the Runoff from Kuhi Taluka



Figure 12: Nitrogen and Phosphorus Load in the Runoff from Maunda Taluka


The average concentration of pollutant in the runoff in Kharif and Rabiseason from different Talukas are presented in Tables 11 and 12.

TABLE 8: Taluka wise Total Runoff in Kharif and RabiSeason

TOTAL RUNOFF (MCM)

TEHSIL

KHARIFSEASON

RABISEASON

Nagpur

6.90

3.41

Kamptee

2.50

5.27

Hingna

8.45

0.77

Katol

8.66

1.78

Narkher

9.46

2.67

Saoner

6.15

1.42

Kalmeshwar

6.57

1.56

Ramtek

4.53

1.39

Parseoni

4.40

3.50

Umrer

5.96

4.73

Bhiwapur

4.91

4.64

Kuhi

6.23

5.14

Maunda

5.77

5.27



Table 9: Excess nutrient N and P load remaining in soil after Kharifcrop

Tehsil

Total N (kg)

Total P (kg)

Total K (kg)

Nagpur

1197010

598505

598505

Kamptee

419620

209810

209810

Higna

1491710

745855

745855

Katol

1495200

747600

747600

Narkher

1642850

821425

821425

Saoner

1034710

517355

517355

Kalmeshwar

1116310

558155

558155

Ramtek

795770

397885

397885

Parseoni

740320

370160

370160

Umrer

1034470

517235

517235

Bhiwapur

824120

412060

412060

Kuhi

1070670

535335

535335

Maunda

1015430

507715

507715

(50% fertilizer remain in the soil and 50% consumed by the plant)
Ref: D. Prasad and E. khan, Environmental Pollution – Land, 46 - 47

Table 10: Excess nutrient N and P load remaining in soil after Rabicrop

Tehsil

Total N (kg)

Total P (kg)

Total K (kg)

Nagpur

480340

309610

228660

Kamptee

736925

484710

359910

Higna

136952.5

83965

73665

Katol

190855

184380

135900

Narkher

311117.5

276605

208095

Saoner

205910

147820

118800

Kalmeshwar

246617.5

163505

135645

Ramtek

220100

133550

106260

Parseoni

489147.5

333735

252945

Umrer

677115

433660

323760

Bhiwapur

649682.5

424045

313845

Kuhi

736520

465120

345150

Maunda

791512.5

492445

379305



Table 11: The average concentration of Nitrogen pollutant in the runoff

Taluka

EMC (N)

Nagpur

0.049

Kamptee

0.039

Higna

0.107

Katol

0.063

Narkher

0.057

Saoner

0.062

Kalmeshwar

0.062

Ramtek

0.059

Parseoni

0.044

Umrer

0.045

Bhiwapur

0.042

Kuhi

0.044

Maunda

0.045



Table 12: The average concentration of Phosphorus pollutant in the runoff

Taluka

EMC (P)

Nagpur

0.020

Kamptee

0.016

Higna

0.045

Katol

0.029

Narkher

0.025

Saoner

0.026

Kalmeshwar

0.026

Ramtek

0.024

Parseoni

0.018

Umrer

0.0180

Bhiwapur

0.017

Kuhi

0.019

Maunda

0.018


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